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Mechanisms of dispersion in a porous medium

Published online by Cambridge University Press:  01 March 2018

M. Dentz*
Affiliation:
Spanish National Research Council, IDAEA-CSIC, c/ Jordi Girona 18, 08034 Barcelona, Spain
M. Icardi
Affiliation:
School of Mathematical Sciences, University of Nottingham, University Park, NG7 2RD Nottingham, UK
J. J. Hidalgo
Affiliation:
Spanish National Research Council, IDAEA-CSIC, c/ Jordi Girona 18, 08034 Barcelona, Spain
*
†Email address for correspondence: marco.dentz@csic.es

Abstract

This paper studies the mechanisms of dispersion in the laminar flow through the pore space of a three-dimensional porous medium. We focus on preasymptotic transport prior to the asymptotic hydrodynamic dispersion regime, in which solute motion may be described by the average flow velocity and a hydrodynamic dispersion coefficient. High-performance numerical flow and transport simulations of solute breakthrough at the outlet of a sand-like porous medium evidence marked deviations from the hydrodynamic dispersion paradigm and identify two distinct regimes. The first regime is characterised by a broad distribution of advective residence times in single pores. The second regime is characterised by diffusive mass transfer into low-velocity regions in the wake of solid grains. These mechanisms are quantified systematically in the framework of a time-domain random walk for the motion of marked elements (particles) of the transported material quantity. Particle transitions occur over the length scale imprinted in the pore structure at random times given by heterogeneous advection and diffusion. Under globally advection-dominated conditions, i.e., Péclet numbers larger than 1, particles sample the intrapore velocities by diffusion and the interpore velocities through advection. Thus, for a single transition, particle velocities are approximated by the mean pore velocity. In order to quantify this advection mechanism, we develop a model for the statistics of the Eulerian velocity magnitude based on Poiseuille’s law for flow through a single pore and for the distribution of mean pore velocities, both of which are linked to the distribution of pore diameters. Diffusion across streamlines through immobile zones in the wake of solid grains gives rise to exponentially distributed residence times that decay on the diffusion time over the pore length. The trapping rate is determined by the inverse diffusion time. This trapping mechanism is represented by a compound Poisson process conditioned on the advective residence time in the proposed time-domain random walk approach. The model is parameterised with the characteristics of the porous medium under consideration and captures both preasymptotic regimes. Macroscale transport is described by an integro-differential equation for solute concentration, whose memory kernels are given in terms of the distribution of mean pore velocities and trapping times. This approach quantifies the physical non-equilibrium caused by a broad distribution of mass transfer time scales, both advective and diffusive, on the representative elementary volume (REV). Thus, while the REV indicates the scale at which medium properties like porosity can be uniquely defined, this does not imply that transport can be characterised by hydrodynamic dispersion.

Information

Type
JFM Papers
Copyright
© 2018 Cambridge University Press 
Figure 0

Figure 1.Three-dimensional (one eighth) sample of the pore space of the medium under investigation and a two-dimensional slice of it.

Figure 1

Figure 2.Three-dimensional snapshots of the complementary residence concentration ($1-c(\boldsymbol{x},t)$) concentration at approximately $t\approx 3\unicode[STIX]{x1D70F}_{u}$ after a constant injection for a Péclet number of 30 (a) and 1000 (b). Flow is from left to right.

Figure 2

Figure 3.Breakthrough curves for $Pe=10^{3}$, $5\times 10^{2}$, $3\times 10^{2}$ and $30$. The dash-dotted lines in the following indicate the numerical data. The solid lines denote the solution (2.7) characterised by the dispersion coefficient ${\mathcal{D}}$ which is directly fitted from the breakthrough data.

Figure 3

Figure 4.(a) The PDFs of (solid) $u_{1}(\boldsymbol{x})$, (dashed) $u_{2}(\boldsymbol{x})$ and (dash-dotted) $u_{3}(\boldsymbol{x})$. (b) The PDFs of the magnitude of Eulerian velocities (circles) and estimation with the velocity model (3.10) for $v_{0}=2.1\langle u_{1}\rangle$ and $\unicode[STIX]{x1D6FC}=2.5$ (dash-dotted). The solid line denotes the PDF (3.14) of mean pore velocities and the dashed line its approximation by (3.16). Velocities are normalised by $\langle u_{1}\rangle$.

Figure 4

Figure 5.The velocity profile across the porous medium perpendicular to the main flow direction.

Figure 5

Figure 6.The dash-dotted line illustrates the PDF of grain diameters (2.3) for $d_{0}=1$ and the solid line shows the corresponding PDF of pore diameters (3.9) for $a_{0}=1$ obtained from the proposed velocity model.

Figure 6

Figure 7.Schematic of transitions in the time-domain random walk model (4.1). The thin red lines represent streamlines of the flow in a cross-section of the porous medium. The shading of the background denotes the absolute value of the flow velocity, which decreases from light to dark; black areas denote the grains. The horizontal arrow denotes particle transitions over the length of a pore in the streamwise direction and the vertical arrow indicates particle transitions across streamlines into low-velocity zones in the wake of the solid grains. Transitions along streamlines are due to mean advection in the pore and diffusion. Transitions across the streamlines are due to diffusion. Particles that enter the immobile zones remain there for the residence time $\unicode[STIX]{x1D70F}_{f}$ before they are released back into the mobile portion of the medium.

Figure 7

Figure 8.Breakthrough curves for $Pe=10^{3}$, $5\times 10^{2}$, $3\times 10^{2}$ and $30$. The symbols denote the breakthrough curves obtained from the TDRW (4.10) based on purely advective transport, $Pe=\infty$, for the transition length $\ell \approx 0.84\ell _{p}$. The dashed lines show the predicted $t^{-2}$ scaling. The TDRW simulations use $10^{9}$ particles.

Figure 8

Figure 9.Breakthrough curves for $Pe=10^{3}$, $3\times 10^{2}$, $30$ and $3$. The dash-dotted lines indicate the numerical data and the symbols the TDRW model for $\ell \approx \ell _{p}$ for $Pe=10^{3}$, $\ell =0.77\ell _{p}$ for $Pe=5\times 10^{2}$ and $Pe=3\times 10^{2}$, and $\ell =0.7\ell _{p}$ for $Pe=30$.

Figure 9

Figure 10.Breakthrough curves for $Pe=10^{3}$, $3\times 10^{2}$, $30$ and $3$. The dash-dotted lines indicate the numerical data and the circles indicate the exponential estimation of the tailing behaviour, from which we obtain the values for $\langle \unicode[STIX]{x1D70F}_{f}\rangle$ and $\unicode[STIX]{x1D6FE}$ displayed in figure 11 below.

Figure 10

Figure 11.(a) Mean trapping time $\langle \unicode[STIX]{x1D70F}_{f}\rangle$ versus $\unicode[STIX]{x1D70F}_{D}$ estimated from the data and (solid line) linear estimation with $r=1/2$. (b) Inverse trapping rate versus $\unicode[STIX]{x1D70F}_{D}$ and linear estimate with $\unicode[STIX]{x1D6FD}=2.5\times 10^{-4}$.

Figure 11

Figure 12.Breakthrough curves for $Pe=10^{3}$, $5\times 10^{2}$, $3\times 10^{2}$ and $30$. The dash-dotted lines indicate the numerical results. The symbols denote the result of the TDRW model including heterogeneous advection and trapping in immobile zones. The TDRW model uses the parameter values given in the captions of figures 9 and 10.