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Occurrence of aromatic amines and N-nitrosamines in the different steps of a drinking water treatment plant

The occurrence of 24 amines within a full scale drinking water treatment plant that used chlorinated agents as disinfectants was evaluated for the first time in this research. Prior to any treatment (raw water), aniline, 3-chloroaniline, 3,4-dichloroaniline and N-nitrosodimethylamine were detected a...

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Published in:Water research (Oxford) 2012-09, Vol.46 (14), p.4543-4555
Main Authors: Jurado-Sánchez, Beatriz, Ballesteros, Evaristo, Gallego, Mercedes
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description The occurrence of 24 amines within a full scale drinking water treatment plant that used chlorinated agents as disinfectants was evaluated for the first time in this research. Prior to any treatment (raw water), aniline, 3-chloroaniline, 3,4-dichloroaniline and N-nitrosodimethylamine were detected at low levels (up to 18 ng/L) but their concentration increased ∼10 times after chloramination while 9 new amines were produced (4 aromatic amines and 5 N-nitrosamines). Within subsequent treatments, there were no significant changes in the amine levels, although the concentrations of 2-nitroaniline, N-nitrosodimethylamine and N-nitrosodiethylamine increased slightly within the distribution system. Eleven of the 24 amines studied were undetected either in the raw and in the treatment plant samples analysed. There is an important difference in the behaviour of the aromatic amines and N-nitrosamines with respect to water temperature and rainfall events. Amine concentrations were higher in winter due to low water temperatures, this effect being more noticeable for N-nitrosamines. Aromatic amines were detected at their highest concentrations (especially 3,4-dichloroaniline and 2-nitroaniline) in treated water after rainfall events. These results may be explained by the increase in the levels of amine precursors (pesticides and their degradation products) in raw water since the rainfall facilitated the transport of these compounds from soil which was previously contaminated as a result of intensive agricultural practices. [Display omitted] ► The occurrence of 24 amines within a drinking water treatment plant was evaluated. ► A systematic study on both daily and seasonal occurrence of the amines was performed. ► Water treatment was not effective for the removal of amines found in untreated water. ► Amine concentrations increased after the chloramination step and new ones appeared. ► Concentrations of amines were the highest during the winter season.
doi_str_mv 10.1016/j.watres.2012.05.039
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Aromatic amines were detected at their highest concentrations (especially 3,4-dichloroaniline and 2-nitroaniline) in treated water after rainfall events. These results may be explained by the increase in the levels of amine precursors (pesticides and their degradation products) in raw water since the rainfall facilitated the transport of these compounds from soil which was previously contaminated as a result of intensive agricultural practices. 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Prior to any treatment (raw water), aniline, 3-chloroaniline, 3,4-dichloroaniline and N-nitrosodimethylamine were detected at low levels (up to 18 ng/L) but their concentration increased ∼10 times after chloramination while 9 new amines were produced (4 aromatic amines and 5 N-nitrosamines). Within subsequent treatments, there were no significant changes in the amine levels, although the concentrations of 2-nitroaniline, N-nitrosodimethylamine and N-nitrosodiethylamine increased slightly within the distribution system. Eleven of the 24 amines studied were undetected either in the raw and in the treatment plant samples analysed. There is an important difference in the behaviour of the aromatic amines and N-nitrosamines with respect to water temperature and rainfall events. Amine concentrations were higher in winter due to low water temperatures, this effect being more noticeable for N-nitrosamines. Aromatic amines were detected at their highest concentrations (especially 3,4-dichloroaniline and 2-nitroaniline) in treated water after rainfall events. These results may be explained by the increase in the levels of amine precursors (pesticides and their degradation products) in raw water since the rainfall facilitated the transport of these compounds from soil which was previously contaminated as a result of intensive agricultural practices. 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identifier ISSN: 0043-1354
ispartof Water research (Oxford), 2012-09, Vol.46 (14), p.4543-4555
issn 0043-1354
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source ScienceDirect Journals
subjects Amines
Amines - analysis
aniline
Applied sciences
Aromatic amines
Chloramines
chlorination
disinfectants
Drinking water
Drinking Water - chemistry
Drinking water treatment plant
Exact sciences and technology
Halogenation
Hydrocarbons, Aromatic - analysis
Low level
N-nitrosamines
N-nitrosodimethylamine
Nitrosamines - analysis
pesticides
Pollution
Precursors
Rain
Rainfall
Rainfall events
Raw
Seasons
soil
Temperature
Water Pollutants, Chemical - analysis
Water Purification - methods
Water temperature
water treatment
Water treatment and pollution
Winter
title Occurrence of aromatic amines and N-nitrosamines in the different steps of a drinking water treatment plant
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