Abstract
Carbonaceous materials have emerged as a method of persulfate activation for remediation. In this study, persulfate activation using powdered activated carbon (PAC) was demonstrated at temperatures relevant to groundwater (5-25°C). At room temperature, increasing doses of PAC (1-20gL-1) led to increased persulfate activation (3.06×10-6s-1 to 2.10×10-4 with 1 and 20gL-1 PAC). Activation slowed at lower temperatures (5 and 11°C); however, substantial (>70 %) persulfate activation was achieved. PAC characterization showed that persulfate is activated at the surface of the PAC, as indicated by an increase in the PAC C:O ratio. Similarly, electron paramagnetic resonance (EPR) spectroscopy studies with a spin trapping agents (5,5-dimethyl-1-pyrroline N-oxide (DMPO)) and 2,2,6,6-tetramethylpiperidine (TEMP) revealed that singlet oxygen was not the main oxidizing species in the reaction. DMPO was oxidized to form 5,5-dimethylpyrrolidone-2(2)-oxyl-(1) (DMPOX), which forms in the presence of strong oxidizers, such as sulfate radicals. The persulfate/PAC system is demonstrated to simultaneously degrade both perfluorooctanoic acid (PFOA) and 1,4-dioxane at room temperature and 11°C. With a 20gL-1 PAC and 75mM persulfate, 80 % and 70 % of the PFOA and 1,4-dioxane, respectively, degraded within 6h at room temperature. At 11°C, the same PAC and persulfate doses led to 57% dioxane degradation and 54 % PFOA degradation within 6h. Coupling PAC with persulfate offers an effective, low-cost treatment for simultaneous destruction of 1,4-dioxane and PFOA.
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