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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 |
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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.
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► 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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[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.</description><identifier>ISSN: 0043-1354</identifier><identifier>EISSN: 1879-2448</identifier><identifier>DOI: 10.1016/j.watres.2012.05.039</identifier><identifier>PMID: 22703862</identifier><identifier>CODEN: WATRAG</identifier><language>eng</language><publisher>Kidlington: Elsevier Ltd</publisher><subject>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</subject><ispartof>Water research (Oxford), 2012-09, Vol.46 (14), p.4543-4555</ispartof><rights>2012 Elsevier Ltd</rights><rights>2015 INIST-CNRS</rights><rights>Copyright © 2012 Elsevier Ltd. All rights reserved.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c515t-575245ddf2475f54f8a77270198ab13ee84e3401326152efe21a1e4ebb7982c03</citedby><cites>FETCH-LOGICAL-c515t-575245ddf2475f54f8a77270198ab13ee84e3401326152efe21a1e4ebb7982c03</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=26137009$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/22703862$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Jurado-Sánchez, Beatriz</creatorcontrib><creatorcontrib>Ballesteros, Evaristo</creatorcontrib><creatorcontrib>Gallego, Mercedes</creatorcontrib><title>Occurrence of aromatic amines and N-nitrosamines in the different steps of a drinking water treatment plant</title><title>Water research (Oxford)</title><addtitle>Water Res</addtitle><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.</description><subject>Amines</subject><subject>Amines - analysis</subject><subject>aniline</subject><subject>Applied sciences</subject><subject>Aromatic amines</subject><subject>Chloramines</subject><subject>chlorination</subject><subject>disinfectants</subject><subject>Drinking water</subject><subject>Drinking Water - chemistry</subject><subject>Drinking water treatment plant</subject><subject>Exact sciences and technology</subject><subject>Halogenation</subject><subject>Hydrocarbons, Aromatic - analysis</subject><subject>Low level</subject><subject>N-nitrosamines</subject><subject>N-nitrosodimethylamine</subject><subject>Nitrosamines - analysis</subject><subject>pesticides</subject><subject>Pollution</subject><subject>Precursors</subject><subject>Rain</subject><subject>Rainfall</subject><subject>Rainfall events</subject><subject>Raw</subject><subject>Seasons</subject><subject>soil</subject><subject>Temperature</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Water Purification - methods</subject><subject>Water temperature</subject><subject>water treatment</subject><subject>Water treatment and pollution</subject><subject>Winter</subject><issn>0043-1354</issn><issn>1879-2448</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2012</creationdate><recordtype>article</recordtype><recordid>eNqNkU2LFDEQhoMo7rj6D0RzEbx0W_nqTl-EZfELFvegew6ZdGXN7HR6TDKK_960PepNPAXC81a91EPIUwYtA9a92rXfbUmYWw6Mt6BaEMM9smG6Hxoupb5PNgBSNEwoeUYe5bwDAM7F8JCccd6D0B3fkLtr544pYXRIZ09tmidbgqN2ChEztXGkH5sYSprz6StEWr4gHYP3WHOF5oKH_CtMxxTiXYi3tFbDRGs9W6aFOextLI_JA2_3GZ-c3nNy8_bN58v3zdX1uw-XF1eNU0yVRvWKSzWOnsteeSW9tn1fC7NB2y0TiFqikMAE75ji6JEzy1DidtsPmjsQ5-TlOveQ5q9HzMVMITvc1w44H7NhwDUIqaX-H1SKWmdQFZUr6uotckJvDilMNv2okFmMmJ1ZjZjFiAFlqpEae3bacNxOOP4J_VZQgRcnwGZn9z7Z6EL-y3VM9ADLoOcr5-1s7G2qzM2nuklVrTBAJyrxeiWwHvdbwGSyC4vZMSR0xYxz-HfXn-OutCs</recordid><startdate>20120915</startdate><enddate>20120915</enddate><creator>Jurado-Sánchez, Beatriz</creator><creator>Ballesteros, Evaristo</creator><creator>Gallego, Mercedes</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>FBQ</scope><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope><scope>7SU</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>KR7</scope></search><sort><creationdate>20120915</creationdate><title>Occurrence of aromatic amines and N-nitrosamines in the different steps of a drinking water treatment plant</title><author>Jurado-Sánchez, Beatriz ; Ballesteros, Evaristo ; Gallego, Mercedes</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c515t-575245ddf2475f54f8a77270198ab13ee84e3401326152efe21a1e4ebb7982c03</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2012</creationdate><topic>Amines</topic><topic>Amines - analysis</topic><topic>aniline</topic><topic>Applied sciences</topic><topic>Aromatic amines</topic><topic>Chloramines</topic><topic>chlorination</topic><topic>disinfectants</topic><topic>Drinking water</topic><topic>Drinking Water - chemistry</topic><topic>Drinking water treatment plant</topic><topic>Exact sciences and technology</topic><topic>Halogenation</topic><topic>Hydrocarbons, Aromatic - analysis</topic><topic>Low level</topic><topic>N-nitrosamines</topic><topic>N-nitrosodimethylamine</topic><topic>Nitrosamines - analysis</topic><topic>pesticides</topic><topic>Pollution</topic><topic>Precursors</topic><topic>Rain</topic><topic>Rainfall</topic><topic>Rainfall events</topic><topic>Raw</topic><topic>Seasons</topic><topic>soil</topic><topic>Temperature</topic><topic>Water Pollutants, Chemical - analysis</topic><topic>Water Purification - methods</topic><topic>Water temperature</topic><topic>water treatment</topic><topic>Water treatment and pollution</topic><topic>Winter</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Jurado-Sánchez, Beatriz</creatorcontrib><creatorcontrib>Ballesteros, Evaristo</creatorcontrib><creatorcontrib>Gallego, Mercedes</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><collection>Environmental Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>Water research (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Jurado-Sánchez, Beatriz</au><au>Ballesteros, Evaristo</au><au>Gallego, Mercedes</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Occurrence of aromatic amines and N-nitrosamines in the different steps of a drinking water treatment plant</atitle><jtitle>Water research (Oxford)</jtitle><addtitle>Water Res</addtitle><date>2012-09-15</date><risdate>2012</risdate><volume>46</volume><issue>14</issue><spage>4543</spage><epage>4555</epage><pages>4543-4555</pages><issn>0043-1354</issn><eissn>1879-2448</eissn><coden>WATRAG</coden><abstract>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.</abstract><cop>Kidlington</cop><pub>Elsevier Ltd</pub><pmid>22703862</pmid><doi>10.1016/j.watres.2012.05.039</doi><tpages>13</tpages></addata></record> |
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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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