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氯化对二级处理出水中溶解性有机物结构的影响
引用本文:薛爽,赵庆良,魏亮亮.氯化对二级处理出水中溶解性有机物结构的影响[J].环境科学,2008,29(4):925-930.
作者姓名:薛爽  赵庆良  魏亮亮
作者单位:1. 哈尔滨工业大学市政环境工程学院,哈尔滨,150090;辽宁大学环境学院,沈阳,110036
2. 哈尔滨工业大学市政环境工程学院,哈尔滨,150090;哈尔滨工业大学城市水资源与环境国家重点实验室,哈尔滨,150090
3. 哈尔滨工业大学市政环境工程学院,哈尔滨,150090
基金项目:教育部长江学者和创新团队支持计划 , 国家重点基础研究发展计划(973计划)
摘    要:以哈尔滨市W污水处理厂污水为研究对象,利用XAD树脂对二级处理出水中的溶解性有机物(DOM)进行分级分离.按照DOM在不同树脂上的吸附特性将其分为5个部分:疏水性有机酸(HPO-A)、疏水性中性有机物(HPO-N)、过渡亲水性有机酸(TPI-A)、过渡亲水性中性有机物(TPI-N)和亲水性有机物(HPI).考察了二级处理出水中有机组分的组成分布、三卤甲烷生成势、紫外光谱和红外光谱.结果表明,二级处理出水中的主要成分是HPO-A和HPI,两者含量之和达70.8%.HPO-A是加氯消毒时产生三卤甲烷的主要有机组分,其三卤甲烷生成活性(STHMFP)为232.9μg/mg.而HPO-N、TPI-A、TPI-N和HPI的STHMFP介于100~125μg/mg之间.氯化反应后,HPO-A、HPO-N、TPI-A和HPI的紫外-可见吸光度均降低,而TPI-N则相反.并且HPO-A、HPO-N、TPI-A和TPI-N中的O-H、C=C和苯环的含量降低,而C-O的含量升高,还生成了C=O和C-Cl.

关 键 词:溶解性有机物  分级  三卤甲烷生成势  三卤甲烷生成活性  红外光谱
文章编号:0250-3301(2008)04-0925-06
收稿时间:2007/4/20 0:00:00
修稿时间:2007年4月20日

Effect of Chlorination on the Structure of Dissolved Organic Matters in Secondary Effluent
XUE Shuang,ZHAO Qing-liang and WEI Liang-liang.Effect of Chlorination on the Structure of Dissolved Organic Matters in Secondary Effluent[J].Chinese Journal of Environmental Science,2008,29(4):925-930.
Authors:XUE Shuang  ZHAO Qing-liang and WEI Liang-liang
Institution:School of Municipal & Environmental Engineering, Harbin Institute of Technology, Harbin 150090, China. xueshuang666@sina.com.cn
Abstract:Dissolved organic matter in the secondary effluent from the W wastewater treatment plant (Harbin) was fractionated using XAD resins into five fractions: hydrophobic acid (HPO-A), hydrophobic neutral (HPO-N), transphilic acid (TPI-A), transphilic neutral (TPI-N) and hydrophilic fraction (HPI). The distribution, trihalomethane formation potential (THMFP), UV-Vis and FTIR spectra of organic fractions in the secondary effluent were examined. XAD fractionation results showed that HPO-A and HPI dominated in the secondary effluent, collectively accounting for about 70.8%. HPO-A was the main precursors for THMFP following chlorination. HPO-A had the highest specific THMFP (STHMFP) and averaged 232.9 microg/mg. The STHMFP of HPO-N, TPI-A, TPI-N and HPI ranged from 100 microg/mg to 125 microg/mg. Chlorination resulted in increased UV-Vis absorbance for TPI-N and decreased UV-Vis absorbance for HPO-A, HPO-N, TPI-A and HPI. After chlorination, O--H, C=C and aromatic ring were found to decrease while C--O was observed to increase for HPO-A, HPO-N, TPI-A and TPI-N. In addition,C=O and C--Cl were found to occur as by-products from the chlorination reaction.
Keywords:dissolved organic matter  fractionation  trihalomethane formation potential  specific trihalomethane formation potential  infrared spectra
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