Department of Civil, Environmental, and Geodetic Engineering at The Ohio State University, USA.
Department of Civil, Environmental, and Geodetic Engineering at The Ohio State University, USA.
Water Res. 2019 May 15;155:86-95. doi: 10.1016/j.watres.2019.02.018. Epub 2019 Feb 20.
In recent years, harmful algal blooms capable of producing toxins including microcystins, cylindrospermopsin, and saxitoxin have increased in occurrence and severity. These toxins can enter drinking water treatment plants and, if not effectively removed, pose a serious threat to human health. The work here investigated the efficacy of permanganate oxidation as a treatment strategy, with a focus on incorporating competition by cyanobacterial cells and dissolved organic matter (DOM). We report rate constants of 272 ± 23 M s for the reaction between permanganate and microcystin-LR, 0.26 ± 0.05 M s for the reaction between permanganate and cylindrospermopsin, and, using chemical analogs, estimate a maximum rate constant of 2.7 ± 0.2 M s for the reaction between permanganate and saxitoxin. We conclude that permanganate only shows potential to remove microcystins. No pH (6-10) or alkalinity (0-50 mM) dependence was observed for the rate of reaction between microcystin-LR and permanganate; however, a temperature dependence was observed and can be characterized by an activation energy of 16 ± 5 kJ mol. The competition posed by cyanobacterial cells was quantified by an apparent second order rate constant of 2.5 ± 0.3 × 10 L μg chl-a s. From this apparent second order rate constant, it was concluded that cyanobacterial cells are not efficient scavengers of permanganate within typical contact times but this second order rate constant can be used to accurately predict microcystin degradation in algal-impacted waters. The competition posed by DOM depended on both the amount of DOM present (as measured by TOC) and its electron donating capacity (as predicted by SUVA-254 or E2/E3 ratio). DOM was concluded to scavenge permanganate efficiently and we forward that this should be considered in permanganate dosing calculations.
近年来,能够产生微囊藻毒素、柱孢藻毒素和石房蛤毒素等毒素的有害藻类水华的发生频率和严重程度都有所增加。这些毒素可能进入饮用水处理厂,如果不能有效去除,将对人类健康构成严重威胁。本工作研究了高锰酸盐氧化作为一种处理策略的效果,重点是纳入蓝藻细胞和溶解有机物 (DOM) 的竞争。我们报告了高锰酸盐与微囊藻毒素-LR 之间反应的速率常数为 272 ± 23 M s,高锰酸盐与柱孢藻毒素之间反应的速率常数为 0.26 ± 0.05 M s,并用化学类似物估计高锰酸盐与石房蛤毒素之间反应的最大速率常数为 2.7 ± 0.2 M s。我们得出结论,高锰酸盐仅显示出去除微囊藻毒素的潜力。没有观察到 pH(6-10)或碱度(0-50 mM)对微囊藻毒素-LR 与高锰酸盐之间反应速率的影响;然而,观察到温度依赖性,可以用 16 ± 5 kJ mol 的活化能来描述。通过微囊藻毒素-LR 与高锰酸盐之间的表观二级反应速率常数 2.5 ± 0.3 × 10 L μg chl-a s 来量化蓝藻细胞造成的竞争。从这个表观二级反应速率常数可以得出结论,蓝藻细胞在典型的接触时间内不是高锰酸盐的有效清除剂,但这个二级反应速率常数可以用来准确预测藻类影响水中的微囊藻降解。DOM 造成的竞争取决于 DOM 的含量(用总有机碳 (TOC) 测量)及其供电子能力(用 SUVA-254 或 E2/E3 比值预测)。DOM 被认为能有效地清除高锰酸盐,我们认为这在高锰酸盐投加计算中应予以考虑。