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Coupled transport and adsorption in graded filters: A multi-scale analysis of non-solenoidal effects

Published online by Cambridge University Press:  26 October 2026

Václav Klika*
Affiliation:
Dept. Mathematics, FNSPE, Czech Technical University in Prague, Prague 120 00, Czech Republic
Vojtěch Kužel
Affiliation:
Dept. Mathematics, FNSPE, Czech Technical University in Prague, Prague 120 00, Czech Republic
*
Corresponding author: Václav Klika, vaclav.klika@fjfi.cvut.cz

Abstract

Content of image described in text.

We investigate the transport and adsorption of solutes within graded porous filters characterised by a spatially varying microstructure. While classical homogenisation theory typically assumes periodic media, we employ the method of multiple scales to derive an effective macroscopic model for ‘near-periodic’ geometries where the porosity varies slowly over the longitudinal coordinate. A key novelty of this work is the departure from the standard solenoidal constraint; instead, we introduce a modified incompressibility condition derived from non-equilibrium thermodynamics that accounts for the coupling between the solute concentration and the solvent velocity. This leads to a generalised Darcy-scale description where the fluid velocity field is non-solenoidal within the porous domain. Through asymptotic analysis, we determine the leading-order concentration profiles and quantify first-order corrections that capture the interplay between the porosity gradient and the mixture composition. We evaluate filter performance across several metrics, including outflux concentration and total adsorption rate, under both fixed-flow and fixed-pressure-drop operating conditions. Our results demonstrate that the porosity gradient and the coupling parameter significantly influence the filtration efficiency, particularly as the medium approaches the clogging limit. The analysis reveals that the optimal filter design is highly sensitive to the chosen performance metric, highlighting the necessity of physically consistent boundary conditions and mixture dynamics in the design of high-efficiency graded filters.

Information

Type
JFM Papers
Copyright
© The Author(s), 2026. Published by Cambridge University Press
Figure 0

Figure 1. Diagram of the filtration model for a two-dimensional square lattice, corresponding to the model description in § 3.1. (a) The physical graded filter is not globally periodic: its porosity varies on the macroscopic scale. (b) For each fixed macroscopic position x$\boldsymbol{x}$, ω(x)$\omega (\boldsymbol{x})$ is the locally periodic reference cell on which the fast-variable corrector problems are posed. Cells at different values of x$\boldsymbol{x}$ need not be identical. Adapted from Dalwadi et al. (2015).

Figure 1

Figure 2. Evaluation of the effective macroscopic transport coefficients as a function of porosity for a two-dimensional square lattice. (a) Diffusion coefficient. The numerical evaluation (dashed line) is obtained by solving the cell problem (3.25) for various porosity values within the range ϕ∈[1−π/4,1]$\phi \in [1-\pi /4,1]$ using the FlexPDE software. The results are then plugged into (3.37) to obtain the plotted values. The closed-form approximation (solid line) represents evaluated expression (4.59). (b) Numerical solution of the cell problem (3.28) yielding the effective permeability coefficient 𝙆=K𝙄d$\unicode{x1D646}=K\unicode{x1D644}_d$ as a function of porosity. The numerical solution requires care and is described in Appendix B.

Figure 2

Figure 3. Numerically obtained (a) fluid-volume averaged solute concentration Cf=C/ϕ$C^{\kern-1pt f}=C/\phi$ and (b) fluid velocity U=ϕUf$U=\phi U^{\kern-1pt f}$ for three gradients m=−0.3,0,0.3$m=-0.3,0,0.3$. The evaluation is performed for a two-dimensional square lattice with the parameters ϕ0=0.75,A=0.6,Pe=3$\phi _0=0.75,\, A=0.6,\, {Pe}=3$ and k=1$k=1$. Note that for the special case of divergence free flow field, A=0$A=0$, the solution is U=1$U=1$ and, hence, it can be viewed as a measure of the effect of the novel term, being a result of treating the filtration problem as a true mixture.

Figure 3

Figure 4. Numerically obtained concentration profiles for linear porosity (4.57) for A=0$A=0$ and A=0.6$A=0.6$, hence, highlighting the effect of the new term. The evaluation is performed for a two-dimensional square lattice with the parameters ϕ0=0.75,Pe=3,k=1$\phi _0=0.75,\, {Pe}=3,\, k=1$ and m=−0.3,0.3$m=-0.3,0.3$. The lower two curves (solid and dashed) correspond to positive porosity gradient m=0.3$m=0.3$, while the upper two to a negative porosity gradient m=−0.3$m=-0.3$. Note that the inlet solute concentration is affected (being larger for A≠0$A\neq 0$) as well as the amount of the particles being filtered out (again, being larger for A≠0$A\neq 0$).

Figure 4

Figure 5. Numerically obtained concentration profiles for linear porosity (4.57) for square and hexagonal lattices in two dimensions. The parameters used are ϕ0=0.75$\phi _0=0.75$, A=0.6,Pe=3,k=1$A=0.6,\, {Pe}=3,\, k=1$ and m=−0.3,0.3$m=-0.3,0.3$. The effect of microscale geometry and the capability of the asymptotic method to reflect these effects in the derived macroscale model is apparent.

Figure 5

Figure 6. (a,b) Asymptotic and numerical concentration profiles for linear porosity given by (4.57). The evaluation is performed for a two-dimensional square lattice with the parameters ϕ0=0.75$\phi _0=0.75$, A=0.6,Pe=3,k=1,m=−0.3$A=0.6, \textit{Pe}=3,\, k=1,\, m=-0.3$ in panel (a) and m=−0.1$m=-0.1$ in panel (b).

Figure 6

Figure 7. We plot two key profiles for efficiency characteristics for the case which was shown in figure 3. In panel (a), we show the adsorption profile λ$\lambda$ and in panel (b), the uniformity of time to local blockage of the filter for linear porosity (4.57). A total measure of the former is in terms of Λ$\varLambda$, while for the latter, we introduced T¯$\overline {T}$ in the text. In panels (c) and (d), we show the same characteristics, but for hexagonal lattice, as in figure 5, where the square lattice is in black curves while the hexagonal lattice in grey.

Figure 7

Figure 8. Numerically obtained two-dimensional square lattice with A=0.6$A=0.6$, Pe=3$ \textit{Pe}=3$ and k=1$k=1$) filter efficiency metrics: (a,b) total adsorption rate per unit time Λ$\varLambda$; (c) uniformity of time to local blockage T¯$\overline {T}$; and (d) filtration capacity per filter lifetime R$R$ for linear porosity (4.57) as a function of the porosity gradient m$m$. Each curve represents a different mean porosity value ϕ0$\phi _0$, starting from ϕ0=0.7$\phi _0=0.7$ for the solid curve, up to ϕ0=0.9$\phi _0=0.9$ (long dashed curve) with steps of 0.05$0.05$. At the same time, m$m$ is continuously varied to observe the effect of filter design. Red curves correspond to A=0$A=0$ (divergence free case), while black curves represent A=0.6$A=0.6$ case. The variation in average porosity ϕ0$\phi _{0}$ is depicted using different types of curve styles as shown in the boxed legend in panel (c).

Figure 8

Figure 9. Numerical results for a two-dimensional square lattice with the parameters A=0.6$A=0.6$, Pe=3$ \textit{Pe}=3$ and k=1$k=1$ are shown. Changes in pressure drop across the filter in the unidirectional filter with linear porosity as a function of the filter design (that is, the slope m$m$ and its average porosity ϕ0$\phi _{0}$). Note that we set Δpref$\Delta p_{\textit{ref}}$ so that it corresponds to the pressure drop with ϕ(x)=0.7−0.023(x−0.5)$\phi (x)=0.7-0.023(x-0.5)$, that is, the minimum on the 0.7$0.7$ branch. The dependence of pressure drop is nonlinear for A≠0$A\neq 0$ and, hence, assessing the appropriate scaling requires to resort to the shooting method solving iterativelly the filter model equations.

Figure 9

Figure 10. Numerically obtained two-dimensional square lattice with Aref=0.6$A_{\textit{ref}}=0.6$, Peref=3$ \textit{Pe}_{\textit{ref}}=3$ and kref=1$k_{\textit{ref}}=1$) filter efficiency metrics for fixed-pressure drop across the filter (obtained by rescaling the fixed-flow problem): (a) total adsorption rate per unit time Λ$\varLambda$; (b) uniformity of time to local blockage T¯$\overline {T}$;and (c) filtration capacity per filter lifetime R$R$ for linear porosity (4.57) as a function of the porosity gradient m$m$. Each curve represents a different mean porosity value ϕ0$\phi _0$, starting from ϕ0=0.7$\phi _0=0.7$ for the solid curve, up to ϕ0=0.9$\phi _0=0.9$ (long dashed curve) with steps of 0.05$0.05$. At the same time, m$m$ is continuously varied to observe the effect of filter design. Red curves correspond to A=0$A=0$ (divergence-free case), while black curves represent the A=0.6$A=0.6$ case. The variation in average porosity ϕ0$\phi _{0}$ is depicted using different types of curve styles, as shown in the boxed legend in panel (b). Note that the location of optimal values of T¯$\overline {T}$ and R$R$ are in a great agreement (with a maximum difference being less than 3%$3\,\%$) suggesting their close relation. In particular, the maxima for R$R$ and A=0$A=0$ are −0.348,−0.233,−0.147,−0.082,−0.038$-0.348,\,-0.233,\,-0.147,\,-0.082,\,-0.038$, while for A=0.6$A=0.6$, we have −0.380,−0.257,−0.159,−0.088,−0.039$-0.380,\,-0.257,\,-0.159,\,-0.088,\,-0.039$. Note that the significance of the mixture composition represented by A≠0$A\neq 0$ is increasing with decreasing porosity.