Treatment of Specific NDMA Precursors by Biofiltration
Removal of targeted N-nitrosodimethylamine (NDMA) precursors during non-optimized biofiltration of tertiary-filtered wastewater was investigated. The study evaluated removal for one spiked model chloramine-reactive precursor—i.e., ranitidine (RAN)—and three spiked model ozone-reactive precursors—i.e...
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Veröffentlicht in: | Journal - American Water Works Association 2017-06, Vol.109 (6), p.E273-E286 |
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creator | MARTI, ERICA J. DICKENSON, ERIC R.V. TRENHOLM, REBECCA A. BATISTA, JACIMARIA R. |
description | Removal of targeted N-nitrosodimethylamine (NDMA) precursors during non-optimized biofiltration of tertiary-filtered wastewater was investigated. The study evaluated removal for one spiked model chloramine-reactive precursor—i.e., ranitidine (RAN)—and three spiked model ozone-reactive precursors—i.e., daminozide (DMZ), 1,1,1′,1′-tetramethyl-4,4′-(methylene-di-p-phenylene)disemicarbazide (TMDS), and 2-furaldehyde dimethylhydrazone (2-F-DMH). Biofiltration was assessed using three parallel, anthracite-containing, 100 mL/min columns operated at three empty bed contact times (EBCTs) of 5, 10, and 20 min. Precursor removals for the 20 EBCT column were not significant for RAN and were up to 80.8 ± 16.2% for DMZ, 26.1 ± 20.6% for 2-F-DMH, and 24.3 ± 10.0% for TMDS. EBCT correlated only with TMDS removal, and dissolved oxygen concentration correlated with 2-F-DMH and TMDS removals, indicating the possible importance of aerobic conditions for these two compounds. Biotransformation was likely the main removal mechanism, and the order for precursor removal was DMZ >> 2-F-DMH ~ TMDS > RAN. |
doi_str_mv | 10.5942/jawwa.2017.109.0070 |
format | Article |
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The study evaluated removal for one spiked model chloramine-reactive precursor—i.e., ranitidine (RAN)—and three spiked model ozone-reactive precursors—i.e., daminozide (DMZ), 1,1,1′,1′-tetramethyl-4,4′-(methylene-di-p-phenylene)disemicarbazide (TMDS), and 2-furaldehyde dimethylhydrazone (2-F-DMH). Biofiltration was assessed using three parallel, anthracite-containing, 100 mL/min columns operated at three empty bed contact times (EBCTs) of 5, 10, and 20 min. Precursor removals for the 20 EBCT column were not significant for RAN and were up to 80.8 ± 16.2% for DMZ, 26.1 ± 20.6% for 2-F-DMH, and 24.3 ± 10.0% for TMDS. EBCT correlated only with TMDS removal, and dissolved oxygen concentration correlated with 2-F-DMH and TMDS removals, indicating the possible importance of aerobic conditions for these two compounds. Biotransformation was likely the main removal mechanism, and the order for precursor removal was DMZ >> 2-F-DMH ~ TMDS > RAN.</description><identifier>ISSN: 0003-150X</identifier><identifier>EISSN: 1551-8833</identifier><identifier>DOI: 10.5942/jawwa.2017.109.0070</identifier><language>eng</language><publisher>Denver: John Wiley and Sons, Inc</publisher><subject>Aerobic conditions ; Anthracite ; Biofilters ; Biofiltration ; Biological Filtration ; Biotransformation ; Correlation analysis ; Dissolved Oxygen ; Empty Bed Contact Time ; Filtered wastewater ; N-Nitrosodimethylamine ; NDMA ; Optimization ; Organic chemicals ; Oxic conditions ; Oxygen ; Ozone ; Peer Reviewed ; potable reuse ; Precursors ; Ranitidine ; Removal ; Wastewater ; Wastewater treatment ; Water treatment</subject><ispartof>Journal - American Water Works Association, 2017-06, Vol.109 (6), p.E273-E286</ispartof><rights>2017 © American Water Works Association</rights><rights>2017 American Water Works Association</rights><rights>Copyright American Water Works Association Jun 2017</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c2790-fa2de27a91e27b455d0192975fca37db93a8ae2b57d782de5fd3556fd03b2ee03</citedby><cites>FETCH-LOGICAL-c2790-fa2de27a91e27b455d0192975fca37db93a8ae2b57d782de5fd3556fd03b2ee03</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/26653539$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/26653539$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,778,782,801,1414,27907,27908,45557,45558,58000,58233</link.rule.ids></links><search><creatorcontrib>MARTI, ERICA J.</creatorcontrib><creatorcontrib>DICKENSON, ERIC R.V.</creatorcontrib><creatorcontrib>TRENHOLM, REBECCA A.</creatorcontrib><creatorcontrib>BATISTA, JACIMARIA R.</creatorcontrib><title>Treatment of Specific NDMA Precursors by Biofiltration</title><title>Journal - American Water Works Association</title><description>Removal of targeted N-nitrosodimethylamine (NDMA) precursors during non-optimized biofiltration of tertiary-filtered wastewater was investigated. The study evaluated removal for one spiked model chloramine-reactive precursor—i.e., ranitidine (RAN)—and three spiked model ozone-reactive precursors—i.e., daminozide (DMZ), 1,1,1′,1′-tetramethyl-4,4′-(methylene-di-p-phenylene)disemicarbazide (TMDS), and 2-furaldehyde dimethylhydrazone (2-F-DMH). Biofiltration was assessed using three parallel, anthracite-containing, 100 mL/min columns operated at three empty bed contact times (EBCTs) of 5, 10, and 20 min. Precursor removals for the 20 EBCT column were not significant for RAN and were up to 80.8 ± 16.2% for DMZ, 26.1 ± 20.6% for 2-F-DMH, and 24.3 ± 10.0% for TMDS. EBCT correlated only with TMDS removal, and dissolved oxygen concentration correlated with 2-F-DMH and TMDS removals, indicating the possible importance of aerobic conditions for these two compounds. Biotransformation was likely the main removal mechanism, and the order for precursor removal was DMZ >> 2-F-DMH ~ TMDS > RAN.</description><subject>Aerobic conditions</subject><subject>Anthracite</subject><subject>Biofilters</subject><subject>Biofiltration</subject><subject>Biological Filtration</subject><subject>Biotransformation</subject><subject>Correlation analysis</subject><subject>Dissolved Oxygen</subject><subject>Empty Bed Contact Time</subject><subject>Filtered wastewater</subject><subject>N-Nitrosodimethylamine</subject><subject>NDMA</subject><subject>Optimization</subject><subject>Organic chemicals</subject><subject>Oxic conditions</subject><subject>Oxygen</subject><subject>Ozone</subject><subject>Peer Reviewed</subject><subject>potable reuse</subject><subject>Precursors</subject><subject>Ranitidine</subject><subject>Removal</subject><subject>Wastewater</subject><subject>Wastewater treatment</subject><subject>Water treatment</subject><issn>0003-150X</issn><issn>1551-8833</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2017</creationdate><recordtype>article</recordtype><recordid>eNqNkF1LwzAUhoMoOKe_QISC160nSdM0l3V-wvwAJ_MupG0CKdsyk47Rf29rh9fe5JDD-5zDeRC6xJAwkZKbRu33KiGAeYJBJAAcjtAEM4bjPKf0GE0AgMaYwdcpOguh6b-Y4XSCsoXXql3rTRs5E31sdWWNraLXu5cieve62vngfIjKLrq1zthV61Vr3eYcnRi1CvriUKfo8-F-MXuK52-Pz7NiHleEC4iNIrUmXAncv2XKWA1YEMGZqRTldSmoypUmJeM1z_soMzVlLDM10JJoDXSKrse5W---dzq0snE7v-lXSiyytD8oJUOKjqnKuxC8NnLr7Vr5TmKQgyD5K0gOgvqWkIOgnhIjtbcr3f0HkcVyWRzYq5FtQuv8H0uyjFFGBf0BNW50mw</recordid><startdate>20170601</startdate><enddate>20170601</enddate><creator>MARTI, ERICA J.</creator><creator>DICKENSON, ERIC R.V.</creator><creator>TRENHOLM, REBECCA A.</creator><creator>BATISTA, JACIMARIA R.</creator><general>John Wiley and Sons, Inc</general><general>American Water Works Association</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7ST</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>K9.</scope><scope>L.G</scope><scope>SOI</scope></search><sort><creationdate>20170601</creationdate><title>Treatment of Specific NDMA Precursors by Biofiltration</title><author>MARTI, ERICA J. ; DICKENSON, ERIC R.V. ; TRENHOLM, REBECCA A. ; BATISTA, JACIMARIA R.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c2790-fa2de27a91e27b455d0192975fca37db93a8ae2b57d782de5fd3556fd03b2ee03</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2017</creationdate><topic>Aerobic conditions</topic><topic>Anthracite</topic><topic>Biofilters</topic><topic>Biofiltration</topic><topic>Biological Filtration</topic><topic>Biotransformation</topic><topic>Correlation analysis</topic><topic>Dissolved Oxygen</topic><topic>Empty Bed Contact Time</topic><topic>Filtered wastewater</topic><topic>N-Nitrosodimethylamine</topic><topic>NDMA</topic><topic>Optimization</topic><topic>Organic chemicals</topic><topic>Oxic conditions</topic><topic>Oxygen</topic><topic>Ozone</topic><topic>Peer Reviewed</topic><topic>potable reuse</topic><topic>Precursors</topic><topic>Ranitidine</topic><topic>Removal</topic><topic>Wastewater</topic><topic>Wastewater treatment</topic><topic>Water treatment</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>MARTI, ERICA J.</creatorcontrib><creatorcontrib>DICKENSON, ERIC R.V.</creatorcontrib><creatorcontrib>TRENHOLM, REBECCA A.</creatorcontrib><creatorcontrib>BATISTA, JACIMARIA R.</creatorcontrib><collection>CrossRef</collection><collection>Aqualine</collection><collection>Environment Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Environment Abstracts</collection><jtitle>Journal - American Water Works Association</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>MARTI, ERICA J.</au><au>DICKENSON, ERIC R.V.</au><au>TRENHOLM, REBECCA A.</au><au>BATISTA, JACIMARIA R.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Treatment of Specific NDMA Precursors by Biofiltration</atitle><jtitle>Journal - American Water Works Association</jtitle><date>2017-06-01</date><risdate>2017</risdate><volume>109</volume><issue>6</issue><spage>E273</spage><epage>E286</epage><pages>E273-E286</pages><issn>0003-150X</issn><eissn>1551-8833</eissn><abstract>Removal of targeted N-nitrosodimethylamine (NDMA) precursors during non-optimized biofiltration of tertiary-filtered wastewater was investigated. The study evaluated removal for one spiked model chloramine-reactive precursor—i.e., ranitidine (RAN)—and three spiked model ozone-reactive precursors—i.e., daminozide (DMZ), 1,1,1′,1′-tetramethyl-4,4′-(methylene-di-p-phenylene)disemicarbazide (TMDS), and 2-furaldehyde dimethylhydrazone (2-F-DMH). Biofiltration was assessed using three parallel, anthracite-containing, 100 mL/min columns operated at three empty bed contact times (EBCTs) of 5, 10, and 20 min. Precursor removals for the 20 EBCT column were not significant for RAN and were up to 80.8 ± 16.2% for DMZ, 26.1 ± 20.6% for 2-F-DMH, and 24.3 ± 10.0% for TMDS. EBCT correlated only with TMDS removal, and dissolved oxygen concentration correlated with 2-F-DMH and TMDS removals, indicating the possible importance of aerobic conditions for these two compounds. Biotransformation was likely the main removal mechanism, and the order for precursor removal was DMZ >> 2-F-DMH ~ TMDS > RAN.</abstract><cop>Denver</cop><pub>John Wiley and Sons, Inc</pub><doi>10.5942/jawwa.2017.109.0070</doi><tpages>14</tpages></addata></record> |
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subjects | Aerobic conditions Anthracite Biofilters Biofiltration Biological Filtration Biotransformation Correlation analysis Dissolved Oxygen Empty Bed Contact Time Filtered wastewater N-Nitrosodimethylamine NDMA Optimization Organic chemicals Oxic conditions Oxygen Ozone Peer Reviewed potable reuse Precursors Ranitidine Removal Wastewater Wastewater treatment Water treatment |
title | Treatment of Specific NDMA Precursors by Biofiltration |
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