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二次废水污水中的 NDMA 形成。

NDMA formation in secondary wastewater effluent.

机构信息

Cranfield Water Science Institute, Cranfield University, Cranfield, Bedfordshire MK43 0AL, UK.

出版信息

Chemosphere. 2013 Mar;91(1):83-7. doi: 10.1016/j.chemosphere.2012.11.003. Epub 2012 Dec 1.

Abstract

Concern over prospective levels of N-nitrosodimethylamine (NDMA) in waters has increased in recent years due to its disinfection byproduct formation potential from chloramination. It has been mooted that this is promoted by organic precursors from municipal wastewaters, such that there is a more significant risk of excessive levels in water reuse applications. Experiments conducted on chloramination and chlorination of secondary wastewater have confirmed that that significant NDMA formation arises only from chloramination, with its concentration varying with test conditions used. A full factor analysis revealed all parameters studied (temperature, pH, monochloramine dose and contact time), both individually and synergistically, to have a statistically significant impact on NDMA formation with contact time being the most important. At raw water temperatures below 10 °C, the NDMA concentration can be minimised to below the 10 ng L(-1) threshold by not exceeding a monochloramine dose of 2 mg L(-1) as Cl(2). However, at higher water temperatures other measures are required to suppress NDMA formation, such as reducing the contact time (which could prove impractical in most applications) or maintaining a pH below 6. Further trials are required to fully develop the operating envelope to ensure NDMA concentrations do not exceed the 10 ng L(-1) threshold, or else to identify effective pretreatment methods for removing the NDMA precursors.

摘要

近年来,由于氯胺消毒副产物形成的潜力,人们对水中 N-亚硝基二甲胺 (NDMA) 的预期水平越来越关注。有人提出,这是由城市废水中的有机前体物促进的,因此在水再利用应用中存在更高水平的风险。对二级废水的氯胺化和氯化实验证实,只有氯胺化才会产生大量的 NDMA,其浓度随所用测试条件的变化而变化。全因子分析表明,所研究的所有参数(温度、pH 值、一氯胺剂量和接触时间)单独或协同作用,对 NDMA 的形成都有统计学意义的影响,其中接触时间是最重要的。在原水温度低于 10°C 的情况下,通过不超过 2mg/L(以 Cl2 计)的一氯胺剂量,可以将 NDMA 浓度最小化至 10ng/L(以 Cl2 计)以下。然而,在较高的水温下,需要采取其他措施来抑制 NDMA 的形成,例如缩短接触时间(这在大多数应用中可能不切实际)或保持 pH 值低于 6。需要进一步的试验来充分开发操作范围,以确保 NDMA 浓度不超过 10ng/L(以 Cl2 计)的阈值,或者确定有效的预处理方法来去除 NDMA 前体物。

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