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This article in JEQ

  1. Vol. 38 No. 3, p. 1274-1285
    Received: July 2, 2008

    * Corresponding author(s): Mats.Larsbo@mark.slu.se
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Simulation of Pharmaceutical and Personal Care Product Transport to Tile Drains after Biosolids Application

  1. Mats Larsbo *a,
  2. David R. Lapenb,
  3. Edward Toppc,
  4. Chris Metcalfed,
  5. Karim C. Abbaspoure and
  6. Kathrin Fenneref
  1. a Dep. of Soil and Environment, Swedish Univ. of Agricultural Sciences (SLU), P.O. Box 7014, 750 07 Uppsala, Sweden
    b Agriculture and Agri-food Canada, Eastern Cereal Oilseed Research Centre, 960 Carling Ave., Ottawa, ON, Canada
    c Agriculture and Agri-food Canada, Southern Crop Protection and Food Research Centre, 1391 Sandford St., London, ON, Canada
    d Water Quality Centre, Trent Univ., Peterborough, ON, Canada
    e Eawag, Swiss Federal Institute for Aquatic Science and Technology, Ueberlandstrasse 133, CH-8600 Dübendorf, Switzerland
    f Institute of Biogeochemistry and Pollutant Dynamics (IBP), ETH Zurich, Universitätsstrasse 16, CH-8092 Zürich, Switzerland


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.

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Copyright © 2009. American Society of Agronomy, Crop Science Society of America, Soil Science SocietyAmerican Society of Agronomy, Crop Science Society of America, and Soil Science Society of America