title: Impact of transverse and longitudinal dispersion on first-order degradation rate constant estimation.
abstract: A two-dimensional analytical model is employed for estimating the first-order degradation rate constant of hydrophobic organic compounds (HOCs) in contaminated groundwater under steady-state conditions. The model may utilize all aqueous concentration data collected downgradient of a source area, but does not require that any data be collected along the plume centerline. Using a least squares fit of the model to aqueous concentrations measured in monitoring wells, degradation rate constants were estimated at a former manufactured gas plant (FMGP) site in the Midwest U.S. The estimated degradation rate constants are 0.0014, 0.0034, 0.0031, 0.0019, and 0.0053 day(-1) for acenaphthene, naphthalene, benzene, ethylbenzene, and toluene, respectively. These estimated rate constants were as low as one-half those estimated with the one-dimensional (centerline) approach of Buscheck and Alcantar [Buscheck, T.E., Alcantar, C.M., 1995. Regression techniques and analytical solutions to demonstrate intrinsic bioremediation. In: Hinchee, R.E., Wilson, J.T., Downey, D.C. (Eds.), Intrinsic Bioremediation, Battelle Press, Columbus, OH, pp. 109-116] which does not account for transverse dispersivity. Varying the transverse and longitudinal dispersivity values over one order of magnitude for toluene data obtained from the FMGP site resulted in nearly a threefold variation in the estimated degradation rate constant-highlighting the importance of reliable estimates of the dispersion coefficients for obtaining reasonable estimates of the degradation rate constants. These results have significant implications for decision making and site management where overestimation of a degradation rate may result in remediation times and bioconversion factors that exceed expectations. For a complex source area or non-steady-state plume, a superposition of analytical models that incorporate longitudinal and transverse dispersion and time may be used at sites where the centerline method would not be applicable.
authors.affiliation: Department of Civil, Construction and Environmental Engineering, Iowa State University, Ames, IA 50011, USA. gastenba@iastate.edu
authors.forename: Greg A
authors.initials: GA
authors.lastname: Stenback
authors.forename: Say Kee
authors.initials: SK
authors.lastname: Ong
authors.forename: Shane W
authors.initials: SW
authors.lastname: Rogers
authors.forename: Bruce H
authors.initials: BH
authors.lastname: Kjartanson
mesh_terms: D007700:Kinetics; D008962:Models, Theoretical; D009930:Organic Chemicals / Q000378:metabolism; D014872:Water Movements; D014874:Water Pollutants, Chemical / Q000378:metabolism*; D014881:Water Supply
chemical_list: D009930:Organic Chemicals; D014874:Water Pollutants, Chemical