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Mass balance analysis of triclosan, diethyltoluamide, crotamiton and carbamazepine in sewage treatment plants
The behavior of antibacterial triclosan, insect-repellent diethyltoluamide (DEET), anticonvulsant carbamazepine, and antipruritic crotamiton was investigated at two sewage treatment plants (STPs) to clarify their complete mass balance. Twenty-four-hour flow-proportional composite samples were collec...
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Published in: | Water science and technology 2010-01, Vol.61 (7), p.1739-1747 |
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description | The behavior of antibacterial triclosan, insect-repellent diethyltoluamide (DEET), anticonvulsant carbamazepine, and antipruritic crotamiton was investigated at two sewage treatment plants (STPs) to clarify their complete mass balance. Twenty-four-hour flow-proportional composite samples were collected from the influent and effluent of primary and final sedimentation tanks, a biofiltration tank and disinfection tanks. Sludge samples (i.e., activated and excess sludge) and samples of the return flow from the sludge treatment process were collected in the same manner. The analytes in both the dissolved and particulate phases were individually determined by a gas chromatograph equipped with mass spectrometer. Triclosan was dominantly detected in the particulate phase especially in the early stage of treatment (up to 83%) and was efficiently removed (over 90%) in STPs, mainly by sorption to sewage sludge. Limited removal was observed for DEET (55+/-24%), while no significant removal was demonstrated for crotamiton or carbamazepine. The solid-water distribution coefficients (K(d), n=4) for triclosan (log K(d): 3.7-5.1), DEET (1.3-1.9) and crotamiton (1.1-1.6) in the sludge samples are also determined in this study. These findings indicate the limitations of current sewage treatment techniques for the removal of these water-soluble drugs (i.e. DEET, carbamazepine, and crotamiton). |
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Twenty-four-hour flow-proportional composite samples were collected from the influent and effluent of primary and final sedimentation tanks, a biofiltration tank and disinfection tanks. Sludge samples (i.e., activated and excess sludge) and samples of the return flow from the sludge treatment process were collected in the same manner. The analytes in both the dissolved and particulate phases were individually determined by a gas chromatograph equipped with mass spectrometer. Triclosan was dominantly detected in the particulate phase especially in the early stage of treatment (up to 83%) and was efficiently removed (over 90%) in STPs, mainly by sorption to sewage sludge. Limited removal was observed for DEET (55+/-24%), while no significant removal was demonstrated for crotamiton or carbamazepine. The solid-water distribution coefficients (K(d), n=4) for triclosan (log K(d): 3.7-5.1), DEET (1.3-1.9) and crotamiton (1.1-1.6) in the sludge samples are also determined in this study. These findings indicate the limitations of current sewage treatment techniques for the removal of these water-soluble drugs (i.e. DEET, carbamazepine, and crotamiton).</description><identifier>ISSN: 0273-1223</identifier><identifier>EISSN: 1996-9732</identifier><identifier>DOI: 10.2166/wst.2010.100</identifier><identifier>PMID: 20371932</identifier><language>eng</language><publisher>England: IWA Publishing</publisher><subject>Activated sludge ; Anti-Bacterial Agents - chemistry ; Anticonvulsants ; Anticonvulsants - chemistry ; Antipruritics - chemistry ; Biofilters ; Biofiltration ; Carbamazepine ; Carbamazepine - chemistry ; Coefficients ; DEET ; DEET - chemistry ; Disinfection ; Drug Residues ; Gas chromatography ; Influents ; Insect Repellents - chemistry ; Mass ; Molecular Structure ; Removal ; Repellents ; Return flow ; Sedimentation ; Sedimentation tanks ; Sewage ; Sewage - chemistry ; Sewage disposal ; Sewage sludge ; Sewage treatment ; Sewage treatment plants ; Sludge ; Sludge treatment ; Tanks ; Toluidines - chemistry ; Triclosan ; Triclosan - chemistry ; Waste Disposal, Fluid - methods ; Wastewater treatment ; Wastewater treatment plants ; Water distribution ; Water engineering ; Water Pollutants, Chemical - chemistry</subject><ispartof>Water science and technology, 2010-01, Vol.61 (7), p.1739-1747</ispartof><rights>Copyright IWA Publishing Apr 2010</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c454t-6dc22d6a0c924050120d00a4f13ddf116920a731e005e3fbbc6049c672c5553f3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27903,27904</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/20371932$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Nakada, N</creatorcontrib><creatorcontrib>Yasojima, M</creatorcontrib><creatorcontrib>Okayasu, Y</creatorcontrib><creatorcontrib>Komori, K</creatorcontrib><creatorcontrib>Suzuki, Y</creatorcontrib><title>Mass balance analysis of triclosan, diethyltoluamide, crotamiton and carbamazepine in sewage treatment plants</title><title>Water science and technology</title><addtitle>Water Sci Technol</addtitle><description>The behavior of antibacterial triclosan, insect-repellent diethyltoluamide (DEET), anticonvulsant carbamazepine, and antipruritic crotamiton was investigated at two sewage treatment plants (STPs) to clarify their complete mass balance. Twenty-four-hour flow-proportional composite samples were collected from the influent and effluent of primary and final sedimentation tanks, a biofiltration tank and disinfection tanks. Sludge samples (i.e., activated and excess sludge) and samples of the return flow from the sludge treatment process were collected in the same manner. The analytes in both the dissolved and particulate phases were individually determined by a gas chromatograph equipped with mass spectrometer. Triclosan was dominantly detected in the particulate phase especially in the early stage of treatment (up to 83%) and was efficiently removed (over 90%) in STPs, mainly by sorption to sewage sludge. Limited removal was observed for DEET (55+/-24%), while no significant removal was demonstrated for crotamiton or carbamazepine. The solid-water distribution coefficients (K(d), n=4) for triclosan (log K(d): 3.7-5.1), DEET (1.3-1.9) and crotamiton (1.1-1.6) in the sludge samples are also determined in this study. These findings indicate the limitations of current sewage treatment techniques for the removal of these water-soluble drugs (i.e. DEET, carbamazepine, and crotamiton).</description><subject>Activated sludge</subject><subject>Anti-Bacterial Agents - chemistry</subject><subject>Anticonvulsants</subject><subject>Anticonvulsants - chemistry</subject><subject>Antipruritics - chemistry</subject><subject>Biofilters</subject><subject>Biofiltration</subject><subject>Carbamazepine</subject><subject>Carbamazepine - chemistry</subject><subject>Coefficients</subject><subject>DEET</subject><subject>DEET - chemistry</subject><subject>Disinfection</subject><subject>Drug Residues</subject><subject>Gas chromatography</subject><subject>Influents</subject><subject>Insect Repellents - chemistry</subject><subject>Mass</subject><subject>Molecular Structure</subject><subject>Removal</subject><subject>Repellents</subject><subject>Return flow</subject><subject>Sedimentation</subject><subject>Sedimentation tanks</subject><subject>Sewage</subject><subject>Sewage - chemistry</subject><subject>Sewage disposal</subject><subject>Sewage sludge</subject><subject>Sewage treatment</subject><subject>Sewage treatment plants</subject><subject>Sludge</subject><subject>Sludge treatment</subject><subject>Tanks</subject><subject>Toluidines - chemistry</subject><subject>Triclosan</subject><subject>Triclosan - chemistry</subject><subject>Waste Disposal, Fluid - methods</subject><subject>Wastewater treatment</subject><subject>Wastewater treatment plants</subject><subject>Water distribution</subject><subject>Water engineering</subject><subject>Water Pollutants, Chemical - chemistry</subject><issn>0273-1223</issn><issn>1996-9732</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2010</creationdate><recordtype>article</recordtype><recordid>eNqFkTtvFUEMhUcIRC6BjhqNREFzN3jemRJFgSAF0UC98s54YaN9XNazii6_nokSKGhS-aHPx5aPEK8VnGnl_ftbLmcaaqUAnoiditE3MRj9VOxAB9Morc2JeMF8AwDBWHguTjSYoKLROzF9QWbZ4YhzIokzjkceWC69LOuQxoVx3ss8UPl5HMsybjgNmfYyrUupaVnmOpNlwrXDCX_TYZhJDrNkusUfVDUIy0RzkYe6oPBL8azHkenVQzwV3z9efru4aq6_fvp88eG6SdbZ0victM4eIUVtwYHSkAHQ9srk3CvlowYMRhGAI9N3XfJgY_JBJ-ec6c2peHeve1iXXxtxaaeBE431CFo2boOz5-dRWfc4aYxRzupYybf_kTfLttaHcauiNSFo8KpS-3uqfoh5pb49rMOE67FV0N751Va_2ju_agMq_uZBdOsmyv_gvwaZPwdekMI</recordid><startdate>20100101</startdate><enddate>20100101</enddate><creator>Nakada, N</creator><creator>Yasojima, M</creator><creator>Okayasu, Y</creator><creator>Komori, K</creator><creator>Suzuki, Y</creator><general>IWA Publishing</general><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>3V.</scope><scope>7QH</scope><scope>7UA</scope><scope>7X7</scope><scope>7XB</scope><scope>88E</scope><scope>8FE</scope><scope>8FG</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>F1W</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>H96</scope><scope>H97</scope><scope>HCIFZ</scope><scope>K9.</scope><scope>L.G</scope><scope>L6V</scope><scope>M0S</scope><scope>M1P</scope><scope>M7S</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><scope>PTHSS</scope><scope>7X8</scope><scope>7QL</scope><scope>7ST</scope><scope>7T7</scope><scope>7TV</scope><scope>8FD</scope><scope>FR3</scope><scope>P64</scope><scope>SOI</scope></search><sort><creationdate>20100101</creationdate><title>Mass balance analysis of triclosan, diethyltoluamide, crotamiton and carbamazepine in sewage treatment plants</title><author>Nakada, N ; Yasojima, M ; Okayasu, Y ; Komori, K ; Suzuki, Y</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c454t-6dc22d6a0c924050120d00a4f13ddf116920a731e005e3fbbc6049c672c5553f3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2010</creationdate><topic>Activated sludge</topic><topic>Anti-Bacterial Agents - 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Twenty-four-hour flow-proportional composite samples were collected from the influent and effluent of primary and final sedimentation tanks, a biofiltration tank and disinfection tanks. Sludge samples (i.e., activated and excess sludge) and samples of the return flow from the sludge treatment process were collected in the same manner. The analytes in both the dissolved and particulate phases were individually determined by a gas chromatograph equipped with mass spectrometer. Triclosan was dominantly detected in the particulate phase especially in the early stage of treatment (up to 83%) and was efficiently removed (over 90%) in STPs, mainly by sorption to sewage sludge. Limited removal was observed for DEET (55+/-24%), while no significant removal was demonstrated for crotamiton or carbamazepine. The solid-water distribution coefficients (K(d), n=4) for triclosan (log K(d): 3.7-5.1), DEET (1.3-1.9) and crotamiton (1.1-1.6) in the sludge samples are also determined in this study. These findings indicate the limitations of current sewage treatment techniques for the removal of these water-soluble drugs (i.e. DEET, carbamazepine, and crotamiton).</abstract><cop>England</cop><pub>IWA Publishing</pub><pmid>20371932</pmid><doi>10.2166/wst.2010.100</doi><tpages>9</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Activated sludge Anti-Bacterial Agents - chemistry Anticonvulsants Anticonvulsants - chemistry Antipruritics - chemistry Biofilters Biofiltration Carbamazepine Carbamazepine - chemistry Coefficients DEET DEET - chemistry Disinfection Drug Residues Gas chromatography Influents Insect Repellents - chemistry Mass Molecular Structure Removal Repellents Return flow Sedimentation Sedimentation tanks Sewage Sewage - chemistry Sewage disposal Sewage sludge Sewage treatment Sewage treatment plants Sludge Sludge treatment Tanks Toluidines - chemistry Triclosan Triclosan - chemistry Waste Disposal, Fluid - methods Wastewater treatment Wastewater treatment plants Water distribution Water engineering Water Pollutants, Chemical - chemistry |
title | Mass balance analysis of triclosan, diethyltoluamide, crotamiton and carbamazepine in sewage treatment plants |
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