• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

N,N-二甲基甲酰胺对污水处理厂和受纳河流中氯胺化生成 N-亚硝基二甲胺的贡献。

Contribution of N,N-dimethylformamide to formation of N-nitrosodimethylamine by chloramination in sewage treatment plants and receiving rivers.

机构信息

Research Center for Environmental Quality Management, Graduate School of Engineering, Kyoto University, 1-2 Yumihama, Otsu, Shiga 520-0811, Japan.

Research Center for Environmental Quality Management, Graduate School of Engineering, Kyoto University, 1-2 Yumihama, Otsu, Shiga 520-0811, Japan.

出版信息

Water Res. 2021 Mar 1;191:116827. doi: 10.1016/j.watres.2021.116827. Epub 2021 Jan 10.

DOI:10.1016/j.watres.2021.116827
PMID:33476799
Abstract

The contribution of specific precursors to N-nitrosodimethylamine formation potential (NDMA FP) upon chloramination depends not only on their NDMA molar yields but also on their concentrations in the actual environment. We investigated the seasonal and diurnal patterns of the NDMA precursor N,N-dimethylformamide (DMF) and NDMA FP in the Yodo River basin, Japan, by examining water samples taken from inside the basin's largest sewage treatment plant (STP) as well as samples from five final effluents from four STPs, two main stream sites, and two tributary sites in the same basin. DMF and NDMA FP were found to be high in influent (raw sewage), and were found to be mostly removed during the STP treatment processes (especially with biological treatment). Nevertheless, DMF was found in concentrations of 0.06 to 31.7 µg/L in chlorinated effluents and in receiving rivers, while NDMA FP was detected in concentrations of 3.57 to 306 ng/L. Thus, STPs were shown to be an important source of DMF and NDMA FP to rivers. A strong positive correlation between NDMA FP and DMF was confirmed in the receiving river (K-M), indicating that DMF was an important NDMA precursor in the Yodo River basin. The contribution of DMF to NDMA FP was 15.8±11.2% (n = 4) in summer and 82.1±10.2% (n = 4) in winter in the main stream (site K-M) of the river due to insufficient dilution of chlorinated effluents from the largest STP. From the viewpoint of NDMA and NDMA FP control at downstream sites, monitoring and control of DMF at upstream sites are important.

摘要

在氯胺消毒过程中,特定前驱物对 N-亚硝基二甲胺形成潜力(NDMA FP)的贡献不仅取决于它们的 NDMA 摩尔产率,还取决于它们在实际环境中的浓度。我们通过检查日本与论河流域最大污水处理厂(STP)内部的水样以及来自四个 STP 的五个最终流出物、两个主要河流站点和同一流域的两个支流站点的水样,研究了 NDMA 前驱物 N,N-二甲基甲酰胺(DMF)和 NDMA FP 的季节性和日变化模式。DMF 和 NDMA FP 在进水(原污水)中含量较高,并且在 STP 处理过程中(特别是在生物处理过程中)大部分被去除。尽管如此,在氯化流出物和受纳河流中仍发现 DMF 的浓度为 0.06 至 31.7 µg/L,而 NDMA FP 的浓度为 3.57 至 306 ng/L。因此,STP 被证明是河流中 DMF 和 NDMA FP 的重要来源。在受纳河流(K-M)中证实了 NDMA FP 和 DMF 之间存在很强的正相关,表明 DMF 是与论河流域中重要的 NDMA 前驱物。由于最大 STP 的氯化流出物稀释不足,DMF 对 NDMA FP 的贡献在夏季为 15.8±11.2%(n=4),在冬季为 82.1±10.2%(n=4)。从下游站点 NDMA 和 NDMA FP 控制的角度来看,监测和控制上游站点的 DMF 非常重要。

相似文献

1
Contribution of N,N-dimethylformamide to formation of N-nitrosodimethylamine by chloramination in sewage treatment plants and receiving rivers.N,N-二甲基甲酰胺对污水处理厂和受纳河流中氯胺化生成 N-亚硝基二甲胺的贡献。
Water Res. 2021 Mar 1;191:116827. doi: 10.1016/j.watres.2021.116827. Epub 2021 Jan 10.
2
Identification of antiyellowing agents as precursors of N-nitrosodimethylamine production on ozonation from sewage treatment plant influent.污水处理厂进水臭氧化过程中作为N-亚硝基二甲胺产生前体的抗黄变剂的鉴定
Environ Sci Technol. 2009 Jul 15;43(14):5236-41. doi: 10.1021/es900227g.
3
Identification of a new N-nitrosodimethylamine precursor in sewage containing industrial effluents.鉴定工业废水污水中的一种新的 N-亚硝基二甲胺前体物。
Environ Sci Technol. 2014 Oct 7;48(19):11243-50. doi: 10.1021/es502284t. Epub 2014 Sep 22.
4
Source of N-nitrosodimethylamine in river waters of the upper Tone River basin in Japan.日本仁淀川水系河水中 N-亚硝基二甲胺的来源。
Water Sci Technol. 2010;62(11):2550-7. doi: 10.2166/wst.2010.519.
5
Characterization of nitrosamines and nitrosamine precursors as non-point source pollutants during heavy rainfall events in an urban water environment.城市水环境暴雨期间亚硝胺及亚硝胺前体物作为非点源污染物的特征分析
J Hazard Mater. 2022 Feb 15;424(Pt C):127552. doi: 10.1016/j.jhazmat.2021.127552. Epub 2021 Oct 20.
6
Impact of biological wastewater treatment on the reactivity of N-Nitrosodimethylamine precursors.生物废水处理对 N-亚硝基二甲胺前体反应性的影响。
Water Res. 2020 Nov 1;186:116315. doi: 10.1016/j.watres.2020.116315. Epub 2020 Aug 18.
7
A nationwide survey of NDMA in raw and drinking water in Japan.日本对原水和饮用水中N-亚硝基二甲胺(NDMA)的全国性调查。
Sci Total Environ. 2009 May 15;407(11):3540-5. doi: 10.1016/j.scitotenv.2009.02.014. Epub 2009 Mar 12.
8
Seasonal and temporal patterns of NDMA formation potentials in surface waters.地表水中 NDMA 形成潜能的季节性和时间性模式。
Water Res. 2015 Feb 1;69:162-172. doi: 10.1016/j.watres.2014.11.017. Epub 2014 Nov 21.
9
Occurrence and formation potential of N-nitrosodimethylamine in ground water and river water in Tokyo.在东京的地下水和河水中 N-亚硝基二甲胺的发生和形成潜力。
Water Res. 2011 May;45(11):3369-77. doi: 10.1016/j.watres.2011.03.053. Epub 2011 Apr 5.
10
N-nitrosomorpholine behavior in sewage treatment plants and urban rivers.亚硝基亚吗啉在污水处理厂和城市河流中的行为。
Water Res. 2019 Oct 15;163:114868. doi: 10.1016/j.watres.2019.114868. Epub 2019 Jul 15.