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Theory and equations

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):

∂(θck)/∂t + ∂(ρsk)/∂t + ∂(avgk)/∂t = ∂/∂x (θ Dkw ∂ck/∂x) + ∂/∂x (av Dkg ∂gk/∂x) − ∂(q ck)/∂x − φk − S cr,k
SymbolMeaning
c, s, gconcentrations in the liquid [M/L³], solid [M/M] and gas [M/L³] phases
ρbulk density [M/L³]
avair content [L³/L³]
qvolumetric water flux [L/T]
Dw, Dgdispersion coefficient in the liquid phase and diffusion coefficient in the gas phase [L²/T]
φreactions: decay and production [M/L³/T]
S crremoval by root uptake (root solute uptake)
knumber 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:

φk = θ(μwck − γwck−1 − μ'w) + ρ(μssk − γssk−1 − μ's) + av(μggk − γggk−1 − μ'g)

Sorption

The adsorption isotherm relating s and c is described by a generalized non-linear equation:

sk = Ks,k ckβk / (1 + ηk ckβk)

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):

gk = kg,k ck

Dispersion

The dispersion coefficient in the liquid phase is

θ Dw = DL |q| + θ Dw τw

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):

τw = θ7/3 / θs2, τg = av7/3 / θs2

or Moldrup et al. (1997); Moldrup et al. (2000).

Boundary conditions

c(x, t) = c0(t) (first type, concentration)
−θ D ∂c/∂x + q c = q0 c0(t) (third type, concentration flux)
∂c/∂x = 0 (zero gradient, bottom only)

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):

−θ D ∂c/∂x + q c = q0 c0 − (Dg/d) (kg c − gatm)

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.