Solute transport equations
Governing equation
The partial differential equations governing one-dimensional advective–dispersive transport of solutes under transient flow in a variably saturated rigid porous medium are, for a chain of decaying solutes Šimůnek et al. (2009); Bear (1972):
| Symbol | Meaning |
|---|---|
| c, s, g | concentrations in the liquid [M/L³], solid [M/M] and gas [M/L³] phases |
| ρ | bulk density [M/L³] |
| av | air content [L³/L³] |
| q | volumetric water flux [L/T] |
| Dw, Dg | dispersion coefficient in the liquid phase and diffusion coefficient in the gas phase [L²/T] |
| φ | reactions: decay and production [M/L³/T] |
| S cr | removal by root uptake (root solute uptake) |
| k | number of the solute in the chain |
The reactions of solute k are first-order decay with the constants μw, μs, μg in the three phases, first-order production from the parent solute k−1 with γw, γs, γg, and zero-order production with μ'w, μ's, μ'g:
Sorption
The adsorption isotherm relating s and c is described by a generalized non-linear equation:
with the empirical coefficients Ks [L³/M], β [–] and η [L³/M]. It simplifies to the Langmuir isotherm (β = 1), the Freundlich isotherm (η = 0) and the linear isotherm (β = 1, η = 0) with the distribution coefficient Kd = Ks. For linear sorption the retardation factor is R = 1 + ρKd/θ.
Gas phase
The concentrations in the liquid and gas phases are related by Henry's law Jury et al. (1983):
Dispersion
The dispersion coefficient in the liquid phase is
with the longitudinal dispersivity DL [L], the molecular diffusion coefficient in free water Dw and the tortuosity factor τw. The tortuosity factors of the liquid and gas phases follow Millington and Quirk (1961):
or Moldrup et al. (1997); Moldrup et al. (2000).
Boundary conditions
The third-type condition at the surface makes the solute enter only with infiltrating water. With volatilization the surface flux additionally contains the diffusion of the gas through a stagnant boundary layer of thickness d Jury et al. (1983):
Non-equilibrium transport
Two-site sorption, mobile–immobile water, dual non-equilibrium and dual-permeability transport are described in non-equilibrium transport; colloids in colloid transport.
Numerical solution
Galerkin finite elements with time weighting ε (Crank–Nicolson by default), optional upstream weighting and artificial dispersion; the time step is limited by the Courant number (numerical solution, discretization).
Literature cited in this topic
- Bear, J. (1972). Dynamics of Fluids in Porous Media. Elsevier, New York, 764 pp.
- Jury, W. A., W. F. Spencer, and W. J. Farmer (1983). Behavior assessment model for trace organics in soil: I. Model description. Journal of Environmental Quality 12(4): 558–564. doi:10.2134/jeq1983.00472425001200040025x
- Millington, R. J., and J. P. Quirk (1961). Permeability of porous solids. Transactions of the Faraday Society 57: 1200–1207. doi:10.1039/TF9615701200
- Moldrup, P., T. Olesen, D. E. Rolston, and T. Yamaguchi (1997). Modeling diffusion and reaction in soils: VII. Predicting gas and ion diffusivity in undisturbed and sieved soils. Soil Science 162(9): 632–640.
- Moldrup, P., T. Olesen, J. Gamst, P. Schjønning, T. Yamaguchi, and D. E. Rolston (2000). Predicting the gas diffusion coefficient in repacked soil: water-induced linear reduction model. Soil Science Society of America Journal 64(5): 1588–1594. doi:10.2136/sssaj2000.6451588x
- Šimůnek, J., M. Šejna, H. Saito, M. Sakai, and M. Th. van Genuchten (2009). The HYDRUS-1D Software Package for Simulating the One-Dimensional Movement of Water, Heat, and Multiple Solutes in Variably-Saturated Media, Version 4.08. HYDRUS Software Series 3, Department of Environmental Sciences, University of California Riverside, Riverside, CA, USA, 330 pp. https://www.pc-progress.com/en/Default.aspx?h1d-description
All sources: References.