Key Laboratory of Drinking Water Science and Technology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China.
Zhuhai Water Environment Holdings Group Ltd., Zhuhai 519000, Guangdong, China.
Environ Sci Technol. 2022 Sep 6;56(17):12278-12287. doi: 10.1021/acs.est.2c03203. Epub 2022 Aug 17.
The oxidation of residual Mn(II) in finished water can lead to MnO deposit formation in drinking water pipes. Previous work has illustrated that microbes readily cause Mn deposit build-up in nondisinfected pipes. Here, we investigated how disinfectant type and dose affected Mn(II) oxidation and MnO accumulation through long-term pipe experiments using water produced by a full-scale water treatment plant. The results showed that Mn(II) oxidation initiated quickly in the new pipes chlorinated with 1.0 mg/L free chlorine. After 130 days of MnO accumulation, 100 μg/L Mn(II) in water could drop to 1.0 μg/L within 1.5 h, resulting from autocatalytic Mn(II) oxidation and Mn(II) adsorption by MnO deposits accumulated on pipe walls. In contrast to chlorination, chloramination (1.0 mg/L Cl) caused almost no MnO accumulation during the entire study period. The underlying mechanism was probably that monochloramine inhibited microbial Mn(II) oxidation without causing significant abiotic Mn(II) oxidation like free chlorine. A low free chlorine dose (0.3 mg/L) also reduced Mn deposit formation by mass but to a lesser extent than chloramination. After disinfection (chlorination or chloramination) was discontinued for days, biotic Mn(II) oxidation occurred, and this process was inhibited again once disinfection was resumed. In addition, Fe(III) of 200 μg/L enhanced the stability of MnO accumulated on pipe surfaces, while humic acid induced MnO deposit resuspension. Overall, this study highlighted the regulating role of disinfectants in MnO formation and provided insights into developing appropriate disinfection strategies for Mn deposit control.
水中残留的 Mn(II) 被氧化后,可能会导致饮用水管道中 MnO 沉积物的形成。先前的研究表明,微生物很容易在未消毒的管道中导致 Mn 沉积物的积累。在这里,我们通过使用大规模水处理厂生产的水进行长期管道实验,研究了消毒剂类型和剂量如何影响 Mn(II) 氧化和 MnO 积累。结果表明,新管道中用 1.0mg/L 自由氯氯化时,Mn(II) 氧化很快开始。在 130 天的 MnO 积累后,水中的 100μg/L Mn(II) 在 1.5 小时内可降至 1.0μg/L,这是由于自动催化的 Mn(II)氧化和 MnO 沉积物在管壁上的吸附。与氯化相比,氯胺化(1.0mg/L Cl)在整个研究期间几乎没有导致 MnO 积累。其潜在机制可能是一氯胺抑制了微生物 Mn(II)氧化,而不像自由氯那样导致显著的非生物 Mn(II)氧化。低剂量的自由氯(0.3mg/L)也减少了 Mn 沉积物的形成,但程度小于氯胺化。消毒(氯化或氯胺化)停止几天后,生物 Mn(II)氧化发生,一旦恢复消毒,该过程再次受到抑制。此外,200μg/L 的 Fe(III)增强了在管道表面上积累的 MnO 的稳定性,而腐殖酸则导致 MnO 沉积物的再悬浮。总的来说,这项研究强调了消毒剂在 MnO 形成中的调节作用,并为开发适当的消毒策略以控制 Mn 沉积物提供了思路。