Graduate Institute of Environmental Engineering, National Taiwan University, No. 1, Sec. 4, Roosevelt Road, Taipei, 10617, Taiwan.
Graduate Institute of Environmental Engineering, National Taiwan University, No. 1, Sec. 4, Roosevelt Road, Taipei, 10617, Taiwan.
Chemosphere. 2016 May;151:332-8. doi: 10.1016/j.chemosphere.2016.02.094. Epub 2016 Mar 15.
Removal of emerging contaminants in wastewater treatment is essential to ensure the ecological health of the receiving water bodies. Ozonation is a promising technology to achieve this purpose but important wastewater characteristics affecting the optimal removal efficiency need to be elucidated. Secondary effluents contain effluent organic matter (EfOM), which can react directly with ozone as well as react as the initiator, promoter and inhibitor in the hydroxyl radical (.OH) chain reactions resulting from ozone decomposition. These different reaction modes of EfOM, coupled with alkalinity and pH value, collectively determine the ozone and .OH exposures and the degradation of pharmaceutical compounds by ozonation. In this study, we determined the rate constants of EfOM collected from two municipal wastewater treatment plants in terms of direct ozone reaction, initiation, promotion and inhibition at various pH values (pH 6.0-7.5) and temperatures (10-30 °C). The rate constants of direct reaction and initiation generally increased with the increasing pH value while the rate constants of promotion and inhibition did not vary significantly. All rate constants increased with the increasing temperature. The removal of ibuprofen, acetylsulfamethoxazole and metoprolol in diluted secondary effluent by ozonation can be fairly-well modeled by using the determined rate constants of EfOM.
去除废水中的新兴污染物对于确保受纳水体的生态健康至关重要。臭氧氧化是实现这一目标的一种很有前途的技术,但需要阐明影响最佳去除效率的重要废水特性。二级出水含有出水有机物 (EfOM),它可以直接与臭氧反应,也可以作为臭氧分解产生的羟基自由基 (•OH) 链式反应的引发剂、促进剂和抑制剂。EfOM 的这些不同反应模式,再加上碱度和 pH 值,共同决定了臭氧和 •OH 的暴露程度以及臭氧氧化对药物化合物的降解程度。在这项研究中,我们测定了从两个城市污水处理厂收集的 EfOM 在不同 pH 值 (pH 6.0-7.5) 和温度 (10-30°C) 下直接臭氧反应、引发、促进和抑制的速率常数。直接反应和引发的速率常数通常随 pH 值的增加而增加,而促进和抑制的速率常数变化不大。所有速率常数都随温度的升高而增加。利用测定的 EfOM 速率常数,可以很好地模拟臭氧氧化稀二级出水中布洛芬、乙酰磺胺甲恶唑和美托洛尔的去除。