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通过催化臭氧化和生物过滤系统,使用合成针铁矿催化剂从受污染水中去除消毒副产物。

Removal of disinfection by-products from contaminated water using a synthetic goethite catalyst via catalytic ozonation and a biofiltration system.

作者信息

Wang Yu-Hsiang, Chen Kuan-Chung

机构信息

Department of Environmental Science and Engineering, National Pingtung University of Science and Technology, Neipu, Pingtung County 912, Taiwan.

出版信息

Int J Environ Res Public Health. 2014 Sep 10;11(9):9325-44. doi: 10.3390/ijerph110909325.

DOI:10.3390/ijerph110909325
PMID:25211774
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC4199022/
Abstract

The effects of synthetic goethite (α-FeOOH) used as the catalyst in catalytic ozonation for the degradation of disinfection by-product (DBP) precursors are investigated. A biofiltration column applied following the catalytic ozonation process is used to evaluate the efficiency of removing DBP precursors via biotreatment. Ozone can rapidly react with aromatic compounds and oxidize organic compounds, resulting in a decrease in the fluorescence intensity of dissolved organic matter (DOM). In addition, catalytic ozonation can break down large organic molecules, which causes a blue shift in the emission-excitation matrix spectra. Water treated with catalytic ozonation is composed of low-molecular structures, including soluble microbial products (SMPs) and other aromatic proteins (APs). The DOM in SMPs and APs is removed by subsequent biofiltration. Catalytic ozonation has a higher removal efficiency for dissolved organic carbon and higher ultraviolet absorbance at 254 nm compared to those of ozonation without a catalyst. The use of catalytic ozonation and subsequent biofiltration leads to a lower DBP formation potential during chlorination compared to that obtained using ozonation and catalytic ozonation alone. Regarding DBP species during chlorination, the bromine incorporation factor (BIF) of trihalomethanes and haloacetic acids increases with increasing catalyst dosage in catalytic ozonation. Moreover, the highest BIF is obtained for catalytic ozonation and subsequent biofiltration.

摘要

研究了合成针铁矿(α-FeOOH)作为催化剂用于催化臭氧化降解消毒副产物(DBP)前体的效果。在催化臭氧化过程之后使用生物过滤柱来评估通过生物处理去除DBP前体的效率。臭氧可与芳香族化合物快速反应并氧化有机化合物,导致溶解有机物(DOM)的荧光强度降低。此外,催化臭氧化可分解大分子有机物质,这会导致发射-激发矩阵光谱发生蓝移。经催化臭氧化处理的水由低分子结构组成,包括可溶性微生物产物(SMPs)和其他芳香族蛋白质(APs)。SMPs和APs中的DOM通过后续生物过滤被去除。与无催化剂的臭氧化相比,催化臭氧化对溶解有机碳的去除效率更高,在254nm处的紫外吸光度也更高。与单独使用臭氧化和催化臭氧化相比,使用催化臭氧化及后续生物过滤可使氯化过程中DBP的生成潜力更低。关于氯化过程中的DBP种类,在催化臭氧化中,三卤甲烷和卤乙酸的溴掺入因子(BIF)随催化剂用量的增加而增加。此外,催化臭氧化及后续生物过滤获得的BIF最高。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/cd6d8a4b692c/ijerph-11-09325-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/03232d33edff/ijerph-11-09325-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/c683cc8cc2c3/ijerph-11-09325-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/8c117a6967cc/ijerph-11-09325-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/2cc26ffdc4a3/ijerph-11-09325-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/086df78aabff/ijerph-11-09325-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/c77f45e4470b/ijerph-11-09325-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/cd6d8a4b692c/ijerph-11-09325-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/03232d33edff/ijerph-11-09325-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/c683cc8cc2c3/ijerph-11-09325-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/8c117a6967cc/ijerph-11-09325-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/2cc26ffdc4a3/ijerph-11-09325-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/086df78aabff/ijerph-11-09325-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/c77f45e4470b/ijerph-11-09325-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2e11/4199022/cd6d8a4b692c/ijerph-11-09325-g007.jpg

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