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Simulation of Pharmaceutical and Personal Care Product Transport to Tile Drains after Biosolids Application
Pharmaceuticals and personal care products (PPCPs) carried in biosolids may reach surface waters or ground water when these materials are applied as fertilizer to agricultural land. During preferential flow conditions created by land application of liquid municipal biosolids (LMB), the residence tim...
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Published in: | Journal of environmental quality 2009-05, Vol.38 (3), p.1274-1285 |
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container_title | Journal of environmental quality |
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creator | Larsbo, Mats Lapen, David R Topp, Edward Metcalfe, Chris Abbaspour, Karim C Fenner, Kathrin |
description | Pharmaceuticals and personal care products (PPCPs) carried in biosolids may reach surface waters or ground water when these materials are applied as fertilizer to agricultural land. During preferential flow conditions created by land application of liquid municipal biosolids (LMB), the residence time of solutes in the macropores may be too short for sorption equilibration. The physically based dual-permeability model MACRO is used in environmental risk assessments for pesticides and may have potential as an environmental risk assessment tool for PPCPs. The objective of this study was to evaluate MACRO and an updated version of MACRO that included non-equilibrium sorption in macropores using data from experiments conducted in eastern Ontario, Canada on the transport of three PPCPs (atenolol, carbamazepine, and triclosan), the nicotine metabolite cotinine, and the strongly sorbing dye rhodamine WT applied in LMB. Results showed that the MACRO model could not reproduce the measured rhodamine WT concentrations (Nash-Sutcliffe coefficient [NS] for the best simulation = -0.057) in drain discharge. The updated version resulted in better fits to measured data for PPCP (average NS = 0.97) and rhodamine WT (NS = 0.84) concentrations. However, it was not possible to simulate all compounds using the same set of hydraulic parameters, which indicates that the model does not fully account for all relevant processes. The results presented herein show that non-equilibrium sorption in macropores has a large impact on simulated solute transport for reactive compounds contained in LMB. This process should be considered in solute transport models that are used for environmental risk assessments for such compounds. |
doi_str_mv | 10.2134/jeq2008.0301 |
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During preferential flow conditions created by land application of liquid municipal biosolids (LMB), the residence time of solutes in the macropores may be too short for sorption equilibration. The physically based dual-permeability model MACRO is used in environmental risk assessments for pesticides and may have potential as an environmental risk assessment tool for PPCPs. The objective of this study was to evaluate MACRO and an updated version of MACRO that included non-equilibrium sorption in macropores using data from experiments conducted in eastern Ontario, Canada on the transport of three PPCPs (atenolol, carbamazepine, and triclosan), the nicotine metabolite cotinine, and the strongly sorbing dye rhodamine WT applied in LMB. Results showed that the MACRO model could not reproduce the measured rhodamine WT concentrations (Nash-Sutcliffe coefficient [NS] for the best simulation = -0.057) in drain discharge. The updated version resulted in better fits to measured data for PPCP (average NS = 0.97) and rhodamine WT (NS = 0.84) concentrations. However, it was not possible to simulate all compounds using the same set of hydraulic parameters, which indicates that the model does not fully account for all relevant processes. The results presented herein show that non-equilibrium sorption in macropores has a large impact on simulated solute transport for reactive compounds contained in LMB. This process should be considered in solute transport models that are used for environmental risk assessments for such compounds.</description><identifier>ISSN: 0047-2425</identifier><identifier>ISSN: 1537-2537</identifier><identifier>EISSN: 1537-2537</identifier><identifier>DOI: 10.2134/jeq2008.0301</identifier><identifier>PMID: 19398526</identifier><identifier>CODEN: JEVQAA</identifier><language>eng</language><publisher>Madison: American Society of Agronomy, Crop Science Society of America, Soil Science Society</publisher><subject>Agricultural land ; Agricultural Science ; Aquatic sciences ; atenolol ; Biosolids ; carbamazepine ; Composting ; Computer Simulation ; Consumer products ; cotinine ; drugs ; dyes ; Environmental assessment ; environmental models ; Environmental risk ; Environmental Sciences related to Agriculture and Land-use ; fertilizer application ; Fish and Aquacultural Science ; Fisk- och akvakulturforskning ; Groundwater ; Household Products - analysis ; hydrologic models ; Jordbruksvetenskap ; macropores ; Metabolites ; Miljö- och naturvårdsvetenskap ; Models, Chemical ; Ontario ; permeability ; personal care products ; Pesticides ; Pharmaceutical Preparations - analysis ; Preferential flow ; rhodamine ; Rhodamines - analysis ; Risk Assessment ; Sewage ; Simulation ; simulation models ; Soils ; Solute transport ; Solutes ; Sorption ; Surface water ; tile drainage ; Tile drains ; triclosan ; Uncertainty ; vadose zone ; Waste Management ; Water Pollutants, Chemical - analysis ; water pollution</subject><ispartof>Journal of environmental quality, 2009-05, Vol.38 (3), p.1274-1285</ispartof><rights>American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America</rights><rights>Copyright American Society of Agronomy May/Jun 2009</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4921-cf64c7d9edb524545681cedb3e5942531723bae6f0da614ce2b962d68fb710b13</citedby><cites>FETCH-LOGICAL-c4921-cf64c7d9edb524545681cedb3e5942531723bae6f0da614ce2b962d68fb710b13</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>230,314,776,780,881,27903,27904</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/19398526$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink><backlink>$$Uhttps://res.slu.se/id/publ/49962$$DView record from Swedish Publication Index$$Hfree_for_read</backlink></links><search><creatorcontrib>Larsbo, Mats</creatorcontrib><creatorcontrib>Lapen, David R</creatorcontrib><creatorcontrib>Topp, Edward</creatorcontrib><creatorcontrib>Metcalfe, Chris</creatorcontrib><creatorcontrib>Abbaspour, Karim C</creatorcontrib><creatorcontrib>Fenner, Kathrin</creatorcontrib><creatorcontrib>Sveriges lantbruksuniversitet</creatorcontrib><title>Simulation of Pharmaceutical and Personal Care Product Transport to Tile Drains after Biosolids Application</title><title>Journal of environmental quality</title><addtitle>J Environ Qual</addtitle><description>Pharmaceuticals and personal care products (PPCPs) carried in biosolids may reach surface waters or ground water when these materials are applied as fertilizer to agricultural land. During preferential flow conditions created by land application of liquid municipal biosolids (LMB), the residence time of solutes in the macropores may be too short for sorption equilibration. The physically based dual-permeability model MACRO is used in environmental risk assessments for pesticides and may have potential as an environmental risk assessment tool for PPCPs. The objective of this study was to evaluate MACRO and an updated version of MACRO that included non-equilibrium sorption in macropores using data from experiments conducted in eastern Ontario, Canada on the transport of three PPCPs (atenolol, carbamazepine, and triclosan), the nicotine metabolite cotinine, and the strongly sorbing dye rhodamine WT applied in LMB. Results showed that the MACRO model could not reproduce the measured rhodamine WT concentrations (Nash-Sutcliffe coefficient [NS] for the best simulation = -0.057) in drain discharge. The updated version resulted in better fits to measured data for PPCP (average NS = 0.97) and rhodamine WT (NS = 0.84) concentrations. However, it was not possible to simulate all compounds using the same set of hydraulic parameters, which indicates that the model does not fully account for all relevant processes. The results presented herein show that non-equilibrium sorption in macropores has a large impact on simulated solute transport for reactive compounds contained in LMB. This process should be considered in solute transport models that are used for environmental risk assessments for such compounds.</description><subject>Agricultural land</subject><subject>Agricultural Science</subject><subject>Aquatic sciences</subject><subject>atenolol</subject><subject>Biosolids</subject><subject>carbamazepine</subject><subject>Composting</subject><subject>Computer Simulation</subject><subject>Consumer products</subject><subject>cotinine</subject><subject>drugs</subject><subject>dyes</subject><subject>Environmental assessment</subject><subject>environmental models</subject><subject>Environmental risk</subject><subject>Environmental Sciences related to Agriculture and Land-use</subject><subject>fertilizer application</subject><subject>Fish and Aquacultural Science</subject><subject>Fisk- och akvakulturforskning</subject><subject>Groundwater</subject><subject>Household Products - analysis</subject><subject>hydrologic models</subject><subject>Jordbruksvetenskap</subject><subject>macropores</subject><subject>Metabolites</subject><subject>Miljö- och naturvårdsvetenskap</subject><subject>Models, Chemical</subject><subject>Ontario</subject><subject>permeability</subject><subject>personal care products</subject><subject>Pesticides</subject><subject>Pharmaceutical Preparations - analysis</subject><subject>Preferential flow</subject><subject>rhodamine</subject><subject>Rhodamines - analysis</subject><subject>Risk Assessment</subject><subject>Sewage</subject><subject>Simulation</subject><subject>simulation models</subject><subject>Soils</subject><subject>Solute transport</subject><subject>Solutes</subject><subject>Sorption</subject><subject>Surface water</subject><subject>tile drainage</subject><subject>Tile drains</subject><subject>triclosan</subject><subject>Uncertainty</subject><subject>vadose zone</subject><subject>Waste Management</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>water pollution</subject><issn>0047-2425</issn><issn>1537-2537</issn><issn>1537-2537</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2009</creationdate><recordtype>article</recordtype><recordid>eNp9kktv1DAUhS0EotOWHWuwWHRFil9x4mU7FGhViak6XVuO44AHJ07tWFX_PY4SgcSChR_X_u658j0G4C1G5wRT9ulgHglC9TmiCL8AG1zSqiB5egk2CLG8Z6Q8AscxHhDCBFX8NTjCgoq6JHwDft3bPjk1WT9A38HdTxV6pU2arFYOqqGFOxOiH3KwVcHAXfBt0hPcBzXE0YcJTh7urTPwc1B2iFB1kwnw0vronW0jvBhHl7XmAqfgVadcNG_W9QQ8fLnab78Vt9-_Xm8vbgvNBMGF7jjTVStM25SElazkNdY5oKYU-S0UV4Q2yvAOtYpjpg1pBCctr7umwqjB9AQUi258MmNq5Bhsr8Kz9MrK6FKjwrzIaCQTOTPzZws_Bv-YTJxkb6M2zqnB-BQlQXVNiZjBD_-AB59C7k2UlHFcU4FYhj4ukA4-xmC6P_UxkrNjcnVMzo5l_N2qmZretH_h1aIMiAV4yl1-_q-YvLm6I_PIB6v4-yW3U16qH8FG-XBP8gXCPP-LCtHfHzusXA</recordid><startdate>200905</startdate><enddate>200905</enddate><creator>Larsbo, Mats</creator><creator>Lapen, David R</creator><creator>Topp, Edward</creator><creator>Metcalfe, Chris</creator><creator>Abbaspour, Karim C</creator><creator>Fenner, Kathrin</creator><general>American Society of Agronomy, Crop Science Society of America, Soil Science Society</general><general>American Society of Agronomy</general><scope>FBQ</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>3V.</scope><scope>7ST</scope><scope>7T7</scope><scope>7TG</scope><scope>7X2</scope><scope>7X7</scope><scope>7XB</scope><scope>88E</scope><scope>88I</scope><scope>8AF</scope><scope>8AO</scope><scope>8C1</scope><scope>8FD</scope><scope>8FE</scope><scope>8FG</scope><scope>8FH</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8G5</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BEC</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>HCIFZ</scope><scope>K9.</scope><scope>KL.</scope><scope>L6V</scope><scope>M0K</scope><scope>M0S</scope><scope>M1P</scope><scope>M2O</scope><scope>M2P</scope><scope>M7S</scope><scope>MBDVC</scope><scope>P64</scope><scope>PATMY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PTHSS</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>S0X</scope><scope>SOI</scope><scope>7U1</scope><scope>7U2</scope><scope>ADTPV</scope><scope>AOWAS</scope></search><sort><creationdate>200905</creationdate><title>Simulation of Pharmaceutical and Personal Care Product Transport to Tile Drains after Biosolids Application</title><author>Larsbo, Mats ; Lapen, David R ; Topp, Edward ; Metcalfe, Chris ; Abbaspour, Karim C ; Fenner, Kathrin</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4921-cf64c7d9edb524545681cedb3e5942531723bae6f0da614ce2b962d68fb710b13</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2009</creationdate><topic>Agricultural land</topic><topic>Agricultural Science</topic><topic>Aquatic sciences</topic><topic>atenolol</topic><topic>Biosolids</topic><topic>carbamazepine</topic><topic>Composting</topic><topic>Computer Simulation</topic><topic>Consumer products</topic><topic>cotinine</topic><topic>drugs</topic><topic>dyes</topic><topic>Environmental assessment</topic><topic>environmental models</topic><topic>Environmental risk</topic><topic>Environmental Sciences related to Agriculture and Land-use</topic><topic>fertilizer application</topic><topic>Fish and Aquacultural Science</topic><topic>Fisk- och akvakulturforskning</topic><topic>Groundwater</topic><topic>Household Products - 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During preferential flow conditions created by land application of liquid municipal biosolids (LMB), the residence time of solutes in the macropores may be too short for sorption equilibration. The physically based dual-permeability model MACRO is used in environmental risk assessments for pesticides and may have potential as an environmental risk assessment tool for PPCPs. The objective of this study was to evaluate MACRO and an updated version of MACRO that included non-equilibrium sorption in macropores using data from experiments conducted in eastern Ontario, Canada on the transport of three PPCPs (atenolol, carbamazepine, and triclosan), the nicotine metabolite cotinine, and the strongly sorbing dye rhodamine WT applied in LMB. Results showed that the MACRO model could not reproduce the measured rhodamine WT concentrations (Nash-Sutcliffe coefficient [NS] for the best simulation = -0.057) in drain discharge. The updated version resulted in better fits to measured data for PPCP (average NS = 0.97) and rhodamine WT (NS = 0.84) concentrations. However, it was not possible to simulate all compounds using the same set of hydraulic parameters, which indicates that the model does not fully account for all relevant processes. The results presented herein show that non-equilibrium sorption in macropores has a large impact on simulated solute transport for reactive compounds contained in LMB. This process should be considered in solute transport models that are used for environmental risk assessments for such compounds.</abstract><cop>Madison</cop><pub>American Society of Agronomy, Crop Science Society of America, Soil Science Society</pub><pmid>19398526</pmid><doi>10.2134/jeq2008.0301</doi><tpages>12</tpages></addata></record> |
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subjects | Agricultural land Agricultural Science Aquatic sciences atenolol Biosolids carbamazepine Composting Computer Simulation Consumer products cotinine drugs dyes Environmental assessment environmental models Environmental risk Environmental Sciences related to Agriculture and Land-use fertilizer application Fish and Aquacultural Science Fisk- och akvakulturforskning Groundwater Household Products - analysis hydrologic models Jordbruksvetenskap macropores Metabolites Miljö- och naturvårdsvetenskap Models, Chemical Ontario permeability personal care products Pesticides Pharmaceutical Preparations - analysis Preferential flow rhodamine Rhodamines - analysis Risk Assessment Sewage Simulation simulation models Soils Solute transport Solutes Sorption Surface water tile drainage Tile drains triclosan Uncertainty vadose zone Waste Management Water Pollutants, Chemical - analysis water pollution |
title | Simulation of Pharmaceutical and Personal Care Product Transport to Tile Drains after Biosolids Application |
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