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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
Main Authors: Larsbo, Mats, Lapen, David R, Topp, Edward, Metcalfe, Chris, Abbaspour, Karim C, Fenner, Kathrin
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cited_by cdi_FETCH-LOGICAL-c4921-cf64c7d9edb524545681cedb3e5942531723bae6f0da614ce2b962d68fb710b13
cites cdi_FETCH-LOGICAL-c4921-cf64c7d9edb524545681cedb3e5942531723bae6f0da614ce2b962d68fb710b13
container_end_page 1285
container_issue 3
container_start_page 1274
container_title Journal of environmental quality
container_volume 38
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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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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