Spatio-temporal variability of non-regulated disinfection by-products within a drinking water distribution network

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• 作者：Catherine Mercier Shanks^a ; ^{catherine.mercier.8@ulaval.ca} ; Jean-Baptiste Sé ; rodes^a ; ^{jean.serodes@gci.ulaval.ca} ; Manuel J. Rodriguez^b ; ^{manuel.rodriguez@esad.ulaval.ca}
• 关键词：Disinfection by-products ; Drinking water ; Haloacetonitrile ; Halonitrometane ; Haloketone ; Water residence time
• 刊名：Water Research
• 出版年：2013
• 出版时间：1 June, 2013
• 年：2013
• 卷：47
• 期：9
• 页码：3231-3243
• 全文大小：959 K

文摘

The non-regulated disinfection by-products (NrDBP) targeted in this study include four haloacetonitriles (trichloroacetonitrile (TCAN); dichloroacetonitrile (DCAN); bromochloroacetonitrile (BCAN) and dibromoacetonitrile (DBAN)); one halonitromethane (trichloronitromethane, better known under the name chloropicrin (CPK)); and two haloketones (1,1-dichloro-2-propanone (11DCPone) and 1,1,1-trichloro-2-propanone (111TCPone)). This study provides a detailed picture of the spatial and temporal variability of these NrDBP concentrations throughout a drinking water distribution system located in a region with major seasonal climate variations. The results obtained show that the concentrations of the investigated NrDBPs varied significantly according to time and location. The average concentrations of TCAN, DCAN, CKP and 111TCPone were significantly higher in summer. Surprisingly, the average concentrations of 11DCPone were significantly higher in winter. For BCAN and DBAN, the average concentrations observed in winter were higher, but not in a statistically significant way. On the other hand, the four HANs, CPK and 111TCPone generally had spatial profiles involving an increase of the concentrations along the network according to increasing water residence times, whereas 11DCPone overall had a profile where concentrations increased at the beginning of the network, followed by a drop in the concentrations towards the ends of the network. In spite of certain disparities in the individual spatio-temporal variation profiles, strong correlations were generally observed between NrDBPs, and trihalomethanes (THMs) and haloacetic acids (HAAs). Therefore, THMs and HAAs could be good statistical indicators of the presence of NrDBPs in the drinking water of the system under study.