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Identification of disinfection by-product precursors by natural organic matter fractionation: a review

期刊

ENVIRONMENTAL CHEMISTRY LETTERS
卷 20, 期 6, 页码 3861-3882

出版社

SPRINGER HEIDELBERG
DOI: 10.1007/s10311-022-01478-x

关键词

Trihalomethanes; Haloacetic acids; Emerging disinfection by-products; Resin fractionation; Membrane fractionation; Chlorination

资金

  1. European Union [847568]
  2. Marie Curie Actions (MSCA) [847568] Funding Source: Marie Curie Actions (MSCA)

向作者/读者索取更多资源

During the disinfection of drinking water, harmful disinfection by-products are produced when natural organic matter reacts with chlorine. Scientists have used fractionation methods to study the reaction process of organic matter. The research found that hydrophilic compounds have higher reactivity towards emerging disinfection by-products. Chlorination time and dose do not affect the reactivity ratio between different fractions.
During disinfection of drinking water, natural organic matter reacts with chlorine to produce harmful disinfection by-products. The identification of precursors of disinfection by-products in natural organic matter is challenging because natural organic matter is very complex and poorly known. Therefore, scientists have focused on the fractionation of natural organic matter with membranes or resins to better understand how and which organic matter fractions react during chlorination. Here, we compared the reactivity of various organic fractions with disinfection by-products. For that we did a meta-analysis of 400 water samples published in 80 publications, with focus on chlorination time and dose, SUVA(254) and the column capacity factor used during resin fractionation. SUVA(254) refers to the ultraviolet absorbance at 254 nm divided by the organic matter concentration. We found that hydrophobic compounds have 10-20% higher reactivity to both trihalomethane and haloacetic acid formation compared to hydrophilic compounds in waters with SUVA(254) above 2L/(mg center dot m), while hydrophobic and hydrophilic compounds have equal reactivity in waters with low SUVA(254). On the other hand, hydrophilic compounds are 20-80% more reactive towards emerging disinfection by-products, regardless of SUVA(254). Chlorination time and dose do not influence the reactivity ratio between the different fractions. An increase in column capacity factor can shift the reactivity ratio from hydrophobic to hydrophilic fractions. Dead-end, stirred cell ultrafiltration membrane fractionation might not always produce sharply separated fractions, which is mainly due to fouling. Therefore, no clear correlation could be found between membrane fractions and all investigated disinfection by-product groups.

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