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Degradation of Dyes by UV/Persulfate and Comparison with Other AOPs: Kinetics and Role of Radicals

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This study investigated the degradation of several dyes (MeB, MeO, RhB) by the UV/PS process. The kinetic degradation of the dyes by this process was also compared with the UV/chlorine and UV/H<sub>2</sub>O<sub>2</sub> processes. The results showed that the dyes were eliminated efficiently using the UV/PS process and the dye degradation in the investigated UV-AOPs followed the first-order kinetic model. The second-order rate constant of the dyes with •OH, SO<sub>4</sub><sup>•-</sup>, and CO<sub>3</sub><sup>•-</sup> were calculated and found to be: <i>k</i><sub>•<i>OH</i>, <i>MeB</i></sub> = 5.6×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub><i>SO</i><sub>4</sub><sup>•-</sup></sub>, <i>MeB</i> = 3.3×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub><i>CO</i><sub>3</sub><sup>•-</sup>, <i>MeO</i></sub>= 6.9×10<sup>7</sup> M<sup>-1</sup>s<sup>-1</sup>; <i>k</i><sub>•<i>OH</i>, <i>MeO</i></sub> = 3.2×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i> <sub><i>SO</i><sub>4</sub><sup>•-</sup>, <i>MeO</i></sub> = 13×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub>CO<sub>3</sub><sup>•-</sup>, <i>MeO</i></sub> = 4.4×10<sup>6</sup> M<sup>-1</sup>s<sup>-1</sup>; <i>k</i><sub>•<i>OH, RhB</i></sub> = 14.8×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub>SO<sub>4</sub><sup>•-</sup>, <i>RhB</i></sub> = 5×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub><i>CO</i><sub>3</sub><sup>•-</sup>, <i>MeO</i></sub> = 1×10<sup>7</sup> M<sup>-1</sup>s<sup>-1</sup>. The steady-state concentrations of •OH and SO<sub>4</sub><sup>•-</sup> were determined using both chemical probes and modeling methods (<i>Kintecus V6.8®</i>), indicating the usefulness of Kintecus <i>V6.8</i>® for estimating the concentration of species in a complex system. The other reactive species were estimated using <i>Kintecus V6.8</i>®, while •OH played a major role for the decomposition of the dyes by UV/H<sub>2</sub>O<sub>2</sub>. The presence of other aqueous components had different impacts on dye degradation: The HCO<sub>3</sub><sup>-</sup> and Cl<sup>-</sup> can promote the degradation efficiency of one dye, but also inhibit the degradation of other dyes. The UV/PS process is more beneficial for TOC removal compared to that of the UV/Chlorine and UV/H<sub>2</sub>O<sub>2</sub> processes for MeO and RhB. In contrast, the TOC removal can be observed higher in the UV/Chlorine and UV/H<sub>2</sub>O<sub>2</sub> processes in the case of MeB degradation. Based on the total cost for electrical energy and oxidant, the UV/PS system showed lower cost than the UV/Chlorine and UV/H<sub>2</sub>O<sub>2</sub> systems for MeO, RhB degradation but higher cost for MeB removal.
Title: Degradation of Dyes by UV/Persulfate and Comparison with Other AOPs: Kinetics and Role of Radicals
Description:
This study investigated the degradation of several dyes (MeB, MeO, RhB) by the UV/PS process.
The kinetic degradation of the dyes by this process was also compared with the UV/chlorine and UV/H<sub>2</sub>O<sub>2</sub> processes.
The results showed that the dyes were eliminated efficiently using the UV/PS process and the dye degradation in the investigated UV-AOPs followed the first-order kinetic model.
The second-order rate constant of the dyes with •OH, SO<sub>4</sub><sup>•-</sup>, and CO<sub>3</sub><sup>•-</sup> were calculated and found to be: <i>k</i><sub>•<i>OH</i>, <i>MeB</i></sub> = 5.
6×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub><i>SO</i><sub>4</sub><sup>•-</sup></sub>, <i>MeB</i> = 3.
3×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub><i>CO</i><sub>3</sub><sup>•-</sup>, <i>MeO</i></sub>= 6.
9×10<sup>7</sup> M<sup>-1</sup>s<sup>-1</sup>; <i>k</i><sub>•<i>OH</i>, <i>MeO</i></sub> = 3.
2×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i> <sub><i>SO</i><sub>4</sub><sup>•-</sup>, <i>MeO</i></sub> = 13×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub>CO<sub>3</sub><sup>•-</sup>, <i>MeO</i></sub> = 4.
4×10<sup>6</sup> M<sup>-1</sup>s<sup>-1</sup>; <i>k</i><sub>•<i>OH, RhB</i></sub> = 14.
8×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub>SO<sub>4</sub><sup>•-</sup>, <i>RhB</i></sub> = 5×10<sup>9</sup> M<sup>-1</sup>s<sup>-1</sup>, <i>k</i><sub><i>CO</i><sub>3</sub><sup>•-</sup>, <i>MeO</i></sub> = 1×10<sup>7</sup> M<sup>-1</sup>s<sup>-1</sup>.
The steady-state concentrations of •OH and SO<sub>4</sub><sup>•-</sup> were determined using both chemical probes and modeling methods (<i>Kintecus V6.
8®</i>), indicating the usefulness of Kintecus <i>V6.
8</i>® for estimating the concentration of species in a complex system.
The other reactive species were estimated using <i>Kintecus V6.
8</i>®, while •OH played a major role for the decomposition of the dyes by UV/H<sub>2</sub>O<sub>2</sub>.
The presence of other aqueous components had different impacts on dye degradation: The HCO<sub>3</sub><sup>-</sup> and Cl<sup>-</sup> can promote the degradation efficiency of one dye, but also inhibit the degradation of other dyes.
The UV/PS process is more beneficial for TOC removal compared to that of the UV/Chlorine and UV/H<sub>2</sub>O<sub>2</sub> processes for MeO and RhB.
In contrast, the TOC removal can be observed higher in the UV/Chlorine and UV/H<sub>2</sub>O<sub>2</sub> processes in the case of MeB degradation.
Based on the total cost for electrical energy and oxidant, the UV/PS system showed lower cost than the UV/Chlorine and UV/H<sub>2</sub>O<sub>2</sub> systems for MeO, RhB degradation but higher cost for MeB removal.

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