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Effect of ozone exposure on the oxidation of trace organic contaminants in wastewater

机译:臭氧暴露对废水中微量有机污染物氧化的影响

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Three tertiary-treated wastewater effluents were evaluated to determine the impact of wastewater quality (i.e. effluent organic matter (EfOM), nitrite, and alkalinity) on ozone (O_3) decomposition and subsequent removal of 31 organic contaminants including endocrine disrupting compounds, Pharmaceuticals, and personal care products. The O_3 dose was normalized based upon total organic carbon (TOC) and nitrite to allow comparison between the different wastewaters with respect to O_3 decomposition. EfOM with higher molecular weight components underwent greater transformation, which corresponded to increased O_3 decomposition when compared on a TOC basis. Hydroxyl radical (OH) exposure, measured by parachlorobenzoic acid (pCBA), showed that limited 'OH was available for contaminant destruction during the initial stage of O_3 decomposition (t < 30 s) due to the effect of the scavenging by the water quality. Advanced oxidation using O_3 and hydrogen peroxide did not increase the net production of 'OH compared to O_3 under the conditions studied. EfOM reactivity impacted the removal of trace contaminants when evaluated based on the O_3:TOC ratio. Trace contaminants with second order reaction rate constants with O_3 (kO_3)>10~5 M~(-1) s~(-1) and 'OH (k_(OH)) > 10~9 M~(-1) s~(-1), including carbamazepine, diclofe-nac, naproxen, sulfamethoxazole, and triclosan, were >95% removed independent of water quality when the O_3 exposure (∫ O_3 dt) was measurable (0-0.8 mgmin/L). O_3 exposure would be a conservative surrogate to assess the removal of trace contaminants that are fast-reacting with O_3. Removal of contaminants with ko_3 < 10 M~(-1) s~(-1) and k_(OH) > 10~9 M~(-1) s~(-1), including atrazine, iopromide, diazepam, and ibuprofen, varied when O_3 exposure could not be measured, and appeared to be dependent upon the compound specific k_(OH). Atrazine, diazepam, ibuprofen and iopromide provided excellent linear correlation with pCBA (R~2 > 0.86) making them good indicators of 'OH availability.
机译:对三种经过三级处理的废水进行了评估,以确定废水质量(即废水中的有机物(EfOM),亚硝酸盐和碱度)对臭氧(O_3)分解的影响,并随后除去31种有机污染物,包括内分泌干扰化合物,药物和个人护理产品。基于总有机碳(TOC)和亚硝酸盐对O_3剂量进行了归一化,以比较不同废水之间的O_3分解。具有较高分子量组分的EfOM经历了更大的转化,这与以TOC为基础的O_3分解相对应。通过对氯苯甲酸(pCBA)测量的羟基自由基(OH)暴露量表明,由于水质清除的影响,在O_3分解的初始阶段(t <30 s),有限的OH可用于污染物的破坏。在研究的条件下,与O_3相比,使用O_3和过氧化氢进行的高级氧化不会增加'OH的净产量。基于O_3:TOC比进行评估时,EfOM反应性影响了痕量污染物的去除。微量污染物具有O_3(kO_3)> 10〜5 M〜(-1)s〜(-1)和'OH(k_(OH))> 10〜9 M〜(-1)s〜的二阶反应速率常数当可测量的O_3暴露量(∫O_3 dt)(0-0.8 mgmin / L)时,(1.9)包括卡马西平,双氯芬酸,萘普生,磺胺甲恶唑和三氯生的去除率> 95%,与水质无关。 O_3暴露将是评估以O_3快速反应的痕量污染物的去除的保守替代方法。去除ko_3 <10 M〜(-1)s〜(-1)和k_(OH)> 10〜9 M〜(-1)s〜(-1)的污染物,包括阿特拉津,碘普罗米特,地西epa和布洛芬当无法测量O_3暴露时,其变化很大,并且似乎取决于化合物的特定k_(OH)。阿特拉津,地西epa,布洛芬和碘普罗米特与pCBA的线性相关性极佳(R〜2> 0.86),使其成为'OH可用性的良好指标。

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