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首页> 外文期刊>Journal of environmental science and health, Part A. Toxic/hazardous substances & environmental engineering >Simultaneous atrazine degradation and E-coli inactivation by simulated solar photo-Fenton-like process using persulfate
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Simultaneous atrazine degradation and E-coli inactivation by simulated solar photo-Fenton-like process using persulfate

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This work evaluated the feasibility of a photo-Fenton-like process using persulfate (PS) and ferrous iron (Fe2+) under simulated solar radiation for degrading the herbicide atrazine (ATZ, 6-Chloro-N-ethyl-N-isopropyl-1,3,5-triazine-2,4-diamine) and inactivating E. coli. Milli Q water, lake water, and diluted wastewater effluents were spiked both simultaneously and separately with ATZ (4mg/L) and E. coli (10(5) CFU/mL), and exposed to treatment. A method for determining the average irradiance throughout the water media in the UV(A+B) range of the Xe lamp emission was developed for bench-scale experiments. These values were used to calculate the UV(A+B) fluences and the solar UV(A+B) energy doses per unit of volume (Q(UV(A+B)), kJ/L). The obtained kinetic data were presented versus energy dose. Treatment of lake water at near-neutral pH was ineffective via the photo-Fenton-like process, attaining only 20 ATZ removal and 1-log reduction of E. coli. In Milli Q water and wastewater, the complete degradation of ATZ in the absence of bacteria was observed at an average energy dose of 1.5kJ/L (60min), while in the presence of cells the degradation efficiency was approximate to 60. When ATZ was present, E. coli inactivation was also affected in Milli Q water, with 1.4-log reduction (93) at a dose of 1.6kJ/L (60min), whereas in wastewater complete inactivation was achieved at a lower dose of 1.3kJ/L (45min). The energy requirements on a Q(UV(A+B)) basis for simultaneous 90 ATZ removal and 99.99 E. coli inactivation in Milli Q water and wastewater were shown to be less than 10kJ/L. This suggests the solar/PS/Fe2+ system is promising for simultaneous treatment and disinfection of wastewater effluents.

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