The Relationship between THMFP and the Variation of Fluorescence Characteristic of DOM among the Different Bio-Treatment Processes

Article Preview

Abstract:

Dissolved organic matter (DOM) from different biological treated wastewater in secondary effluent of different municipal wastewater treated plants are isolated and fractionated using resin adsorption into five different fractions: hydrophobic bases (HOB), hydrophobic acids (HOA), hydrophilic bases (HIB), hydrophilic acids (HIA) and hydrophilic neutrals (HIN). The characteristics of three dimensional excitation emission matrix fluorescence spectroscopy (3DEEM) and disinfection by-products formation potential (THMFP) of each fraction are investigated. The objective of this study is to investigate the influence of different biological processes on THMs generation and transformation. The results show that for each municipal wastewater treated plant, HIA and HOA fractions content more fulvic-like acid and humic-like acid, which are the important matter to result the higher THMFP. THMFP of HIA rang from 736μg/L to 359μg/L in the secondary effluent. It shows that acidic organic matters are important THMs precursors, especially fulvic-like acids and humic-like acids. The Orbal oxidation ditch process can lead to the highest THMFP, and secondly is the Convert A2/O process.

You might also be interested in these eBooks

Info:

Periodical:

Advanced Materials Research (Volumes 356-360)

Pages:

2042-2046

Citation:

Online since:

October 2011

Authors:

Export:

Price:

Permissions CCC:

Permissions PLS:

Сopyright:

© 2012 Trans Tech Publications Ltd. All Rights Reserved

Share:

Citation:

[1] Qingliang Zhao, Ting Jia, Liangliang Wei et al. Fluorescence characterization of the reactivity of THMs precursors in secondary effluent (In Chinese). China Environmental Science, 2009,29(11):1164~1170

Google Scholar

[2] Ruixia Hao, Kexin Cao,Yi Deng et al. Characterization of dissolved organic pollutants in wastewater by three-dimensional fluorescent spectroscopy. (In Chinese) Chinese Journal of Analysis Laboratory, 2007,10(26):41~44

Google Scholar

[3] Lheer J. A. Comprehensive approach to preparative isolation and fractionation of dissolved organic carbon from natural waters and wastewaters. (In Chinese) Environ. Sci. Technol, 1981, 15:578-587

DOI: 10.1021/es00087a010

Google Scholar

[4] Shuang Xue, Lei Liang, Qiangliang Zhao et al.Fluorescence Characteristics of Dissolved Organic Matter in Secondary Treated Effluents (In Chinese). Environmental Science & Technology, 2010,30(7):77~182

Google Scholar

[5] Yingxue Sun,Qianyuan Wu, Jie Tian et al.Characteristics and Chlorinated Disinfection By-products Formation Potential of Dissolved Organic Matter Fractions in Treated Wastewater(In Chinese). Environmental Science, 2009,30(8):2282-2287

Google Scholar

[6] Trehy M L, Yost R A, Miles C J. Chlorination byproducts of aminoacids in natural waters.Environ Sci Technol,1986,20(11):1117-1122

DOI: 10.1021/es00153a006

Google Scholar

[7] Rittmann B E,Bac W, Namkung E, et al. A critical evaluation of microbial product formation in biological processes.Water Sci Technol,1987.19(7):517-528

DOI: 10.2166/wst.1987.0231

Google Scholar

[8] Chang E E, Chiang P C, Ko Y W , et al. Characteristics of orangic precursors and their relationship with disinfection by-products,Chemosphere, 2001,44(5):1231-1236

DOI: 10.1016/s0045-6535(00)00499-9

Google Scholar

[9] Kim H C, Yu M J,Han L. Muulti-method study of the characteristic chemical nature of aquatic humic substances isolated from the Han River, Korea. Applied Geochemestry, 2006, 21(7):1226-1239

DOI: 10.1016/j.apgeochem.2006.03.011

Google Scholar