首页 | 本学科首页   官方微博 | 高级检索  
     检索      

AAO-MBR工艺污水处理系统中消毒副产物前体物变化规律
引用本文:张雅晶,缪恒锋,张晓夏,周梦娟,阮文权.AAO-MBR工艺污水处理系统中消毒副产物前体物变化规律[J].环境科学研究,2018,31(12):2037-2046.
作者姓名:张雅晶  缪恒锋  张晓夏  周梦娟  阮文权
作者单位:1.江南大学环境与土木工程学院, 江苏 无锡 214122
基金项目:国家水体污染控制与治理科技重大专项(No.2017ZX07203-003)
摘    要:为探究DBPs(消毒副产物)前体物在污水处理过程中的变化情况,采用超滤膜和XAD大孔吸附树脂将AAO-MBR工艺沿程出水中DOM(溶解性有机物)进行分离,并利用3D-EEM(三维荧光光谱)对分离前后水样进行表征,同时测定DBPFP(消毒副产物生成势).结果表明:①沉砂池出水具有较低的C-DBPFP(含碳消毒副产物生成势);经过AAO和MBR后,由于微生物代谢作用生成的疏水性SMPs(微生物代谢产物)类物质(为主要的C-DBPs前体物质)包含较多不饱和键,导致C-DBPFP增加.②沉砂池出水的N-DBPFP(含氮消毒副产物生成势)较低,但经过AAO后生成的小分子物质(为主要的N-DBPs前体物)导致N-DBPFP增加;经过MBR后由于SRT(污泥停留时间)和污泥浓度的增加造成小分子物质减少,致使N-DBPFP降低.③市政污水经过AAO后,C-DBPs和N-DBPs前体物分别增加了90.9%和7.3%;而MBR具有较高的DOC去除率(74.4%),去除了56.8%的C-DBPs前体物和78.1%的N-DBPs前体物.研究显示,AAO-MBR工艺对市政污水中C-DBPs和N-DBPs前体物有较好地去除效果. 

关 键 词:消毒副产物前体物    AAO-MBR工艺    三维荧光光谱    分子量分离    亲疏水性分离
收稿时间:2018/4/3 0:00:00
修稿时间:2018/7/11 0:00:00

Variation of Disinfection By-Product Precursors during Anaerobic-Anoxic-Oxic-Membrane-Bioreactor (AAO-MBR) Process in the Sewage Treatment Plant
ZHANG Yajing,MIAO Hengfeng,ZHANG Xiaoxi,ZHOU Mengjuan and RUAN Wenquan.Variation of Disinfection By-Product Precursors during Anaerobic-Anoxic-Oxic-Membrane-Bioreactor (AAO-MBR) Process in the Sewage Treatment Plant[J].Research of Environmental Sciences,2018,31(12):2037-2046.
Authors:ZHANG Yajing  MIAO Hengfeng  ZHANG Xiaoxi  ZHOU Mengjuan and RUAN Wenquan
Institution:1.School of Environmental & Civil Engineering, Jiangnan University, Wuxi 214122, China2.Jiangsu Key Laboratory of Anaerobic Biotechnology, Wuxi 214122, China3.Jiangsu Collaborative Innovation Center of Technology and Material of Water Treatment, Suzhou 215009, China
Abstract:In order to investigate the change of disinfection by-product (DBP) precursors during the sewage treatment process, dissolved organic matter (DOM) of the effluents during the AAO-MBR process was separated with ultrafiltration membrane and XAD adsorption resin, then characterized with 3D-EEM spectra. The DBPFP of effluents and their separated fractions were further evaluated in this study. The results showed that C-DBPFP of the grit chamber effluent was low, the AAO and MBR processes could increase C-DBPFP significantly. SMPs produced by microbial metabolism during the AAO and MBR processes was the major C-DBP precursors. The grit chamber effluent also displayed low N-DBPFP. The AAO process led to the increase in N-DBPFP mainly due to the production of small molecule SMPs. The MBR process could result in the decrease in N-DBPFP comparing to the AAO process, by reducing small molecule SMPs with long SRT and high sludge concentration. In all, the AAO process would obviously enhance C-DBP and N-DBP precursors by 90.9% and 7.3%, respectively. However, the MBR process could remove 74.4% DOC, resulting in 56.8% C-DBP precursor and 78.1% N-DBP precursor removal. Therefore, AAO-MBR had a respectable removal effect on C and N-DBPs precursors in the municipal sewage.
Keywords:disinfection by-product precursors  AAO-MBR process  3D-EEM (fluorescence excitation emission matrix)  molecular weight distribution  hydrophobic-based fraction
本文献已被 CNKI 等数据库收录!
点击此处可从《环境科学研究》浏览原始摘要信息
点击此处可从《环境科学研究》下载免费的PDF全文
设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号