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Coupling rheology and segregation in granular flows

Published online by Cambridge University Press:  29 December 2020

T. Barker
Affiliation:
Department of Mathematics and Manchester Centre for Nonlinear Dynamics, University of Manchester, Oxford Road, Manchester M13 9PL, UK School of GeoSciences and Institute for Infrastructure and Environment, University of Edinburgh, King's Buildings, Edinburgh EH9 3JL, UK
M. Rauter
Affiliation:
Department of Natural Hazards, Norwegian Geotechnical Institute, Oslo N-0806, Norway Department of Mathematics, University of Oslo, Oslo N-0851, Norway
E. S. F. Maguire
Affiliation:
Department of Mathematics and Manchester Centre for Nonlinear Dynamics, University of Manchester, Oxford Road, Manchester M13 9PL, UK
C. G. Johnson
Affiliation:
Department of Mathematics and Manchester Centre for Nonlinear Dynamics, University of Manchester, Oxford Road, Manchester M13 9PL, UK
J. M. N. T. Gray*
Affiliation:
Department of Mathematics and Manchester Centre for Nonlinear Dynamics, University of Manchester, Oxford Road, Manchester M13 9PL, UK
*
†Email address for correspondence: nico.gray@manchester.ac.uk

Abstract

During the last fifteen years there has been a paradigm shift in the continuum modelling of granular materials; most notably with the development of rheological models, such as the $\mu (I)$-rheology (where $\mu$ is the friction and I is the inertial number), but also with significant advances in theories for particle segregation. This paper details theoretical and numerical frameworks (based on OpenFOAM) which unify these currently disconnected endeavours. Coupling the segregation with the flow, and vice versa, is not only vital for a complete theory of granular materials, but is also beneficial for developing numerical methods to handle evolving free surfaces. This general approach is based on the partially regularized incompressible $\mu (I)$-rheology, which is coupled to the gravity-driven segregation theory of Gray & Ancey (J. Fluid Mech., vol. 678, 2011, pp. 353–588). These advection–diffusion–segregation equations describe the evolving concentrations of the constituents, which then couple back to the variable viscosity in the incompressible Navier–Stokes equations. A novel feature of this approach is that any number of differently sized phases may be included, which may have disparate frictional properties. Further inclusion of an excess air phase, which segregates away from the granular material, then allows the complex evolution of the free surface to be captured simultaneously. Three primary coupling mechanisms are identified: (i) advection of the particle concentrations by the bulk velocity, (ii) feedback of the particle-size and/or frictional properties on the bulk flow field and (iii) influence of the shear rate, pressure, gravity, particle size and particle-size ratio on the locally evolving segregation and diffusion rates. The numerical method is extensively tested in one-way coupled computations, before the fully coupled model is compared with the discrete element method simulations of Tripathi & Khakhar (Phys. Fluids, vol. 23, 2011, 113302) and used to compute the petal-like segregation pattern that spontaneously develops in a square rotating drum.

Information

Type
JFM Papers
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited.
Copyright
© The Author(s), 2020. Published by Cambridge University Press
Figure 0

Table 1. The frictional parameters $\mu _s$, $\mu _d$, $\mu _{\infty }$, $I_0$ and $\alpha$ in Barker & Gray's (2017) friction law, which were measured for $143\ \mathrm {\mu }\textrm {m}$ glass beads. The value $I_1\simeq I_1^{N}$ is set by the lower bound for well posedness in Jop et al.'s (2006) friction law using the parameters above. Unless stated otherwise, the remaining parameters are the values chosen in the numerical simulations. Note that the air viscosity is higher than the physical value of $\eta _*^{a}=1.81\times 10^{-5}\ \textrm {kg}\,(\textrm {ms})^{-1}$ to prevent the convective Courant number limiting the time-step size.

Figure 1

Figure 1. Comparison between the friction law of Jop et al. (2006) (red line) and the partially regularized law of Barker & Gray (2017) (blue line). The Jop et al. (2006) curve has a finite yield stress $\mu _s$ (red dot) and asymptotes to $\mu _d$ at large inertial number (dashed line). For the parameters summarized in table 1, it is well posed in the range $[I_1^{N},I_2^{N}]= [0.00397, 0.28016]$ (red shaded region). A necessary condition for well posedness is that the friction $\mu$ is zero at $I=0$ (blue dot). Barker & Gray's (2017) curve therefore introduces a creep state for $I\in [0,I_1]$ to the left of the green dot (see inset) and becomes linear at large inertial numbers. The value of $I_1=0.004$ is chosen to be very slightly larger than $I_1^{N}$. The resulting partially regularized law is well posed for $I\in [0, 16.9918]$.

Figure 2

Table 2. Non-dimensional constants $\mathcal {A}$, $\mathcal {B}$, $\mathcal {C}$ and $\mathcal {E}$ in the diffusion (3.7) and segregation laws (3.9) of Trewhela et al. (2021).

Figure 3

Table 3. Constant segregation velocities and diffusivities between the different phases, as well as the inflow thickness $h$ for the inclined flow simulations presented in §§ 5 and 6.

Figure 4

Figure 2. The air fraction $\varphi ^{a}$ after $t=0.05\ \textrm {s}$ of injection of granular material onto a frictional plane inclined at $\zeta =24^{\circ }$. Case $(a)$ uses no interface sharpening whereas case $(b)$ uses the usual counter-gradient transport method often employed in OpenFOAM. For the same initial and boundary conditions, the air segregation method proposed in § 4 gives the constituent distribution shown in panel $(c)$, using the parameters in table 3.

Figure 5

Figure 3. Evolution of a granular flow front down a frictional plane inclined at $\zeta =24^{\circ }$. The flow consists of a bidisperse mixture with both small and large particles having identical rheological properties (listed in table 1) and no feedback from the local particle size. Here the concentration of small particles $\varphi ^{s}$ is plotted inside the granular material at 5 successive times. The plots are stretched vertically in order to provide greater detail of the concentration distribution. Panel $(e)$, which is the plot of a late time at $t=10\ \textrm {s}$, is indicative of the long-time steady dynamics after which no further evolution is observed in the simulations. The dashed lines in (e) show the corresponding shock solutions of Gray & Thornton (2005), which assume that there is no diffusion and resolve only the normal component of the segregation flux. The parameters are summarized in tables 1 and 3. A supplementary movie 1 is available at https://doi.org/10.1017/jfm.2020.973 showing the full dynamics of the flow front.

Figure 6

Figure 4. Long-time downstream velocity and small particle concentration. Open circles are from the numerical simulation, at the outflow boundary $x=L_x$ at $t=10\ \textrm {s}$, and the solid curve in $(a)$ is the Bagnold velocity profile (5.4) and in $(b)$ the solid line is the exact solution (5.8)–(5.11) of Gray & Chugunov (2006). The parameters are summarized in tables 1 and 3.

Figure 7

Figure 5. Comparison of the two-dimensional computed steady travelling free-surface profile (red line), with solutions of the depth-averaged equations using the regularized effective basal friction law (5.21) with a plug-flow shape factor $\chi =1$ (black dashed line) and Bagnold flow shape factor $\chi =5/4$ (blue dashed line). The free surface from the full two-dimensional numerics, after $t=10\ \textrm {s}$ in a moving frame, is calculated by interpolating the contour of $\varphi ^{a}=0$. The parameters are summarized in table 1.

Figure 8

Figure 6. Flow fields inside the granular flow front after $10\ \textrm {s}$ in a moving frame. Panels (a,b) show the velocity components and panel $(c)$ is a selection of the corresponding streamlines. The pressure and the base 10 logarithm of the inertial number $I$ are shown in (d,e) respectively. Note that the downstream velocity in panel (a) has been shifted by the front velocity (5.16) in order to give values in the frame of the frictional base. The parameters are summarized in table 1.

Figure 9

Figure 7. Exact solutions for (a) the inertial number and (b) the downstream velocity for a bidisperse mixture of large and small particles (black lines) on a slope inclined at $\zeta =24^{\circ }$ to the horizontal. The solutions assume a small particle concentration profile given by Gray & Chugunov's (2006) exact solution in (5.8)–(5.11), with $\overline {\varphi ^{s}}=0.5$ and using the parameters in table 3. Here, all bulk flow parameters are identical to those in table 1 except that the large particles have $\mu _{s}^{l}=1.2\mu _{s}$ and $\mu _{\infty }^{\nu }=0$ for both phases. The dashed lines indicate uniform concentration solutions with red corresponding to pure large, blue corresponding to pure small particles and green being the solution for a mixture with $\varphi ^{s}=0.5$ everywhere.

Figure 10

Figure 8. Contour plots of (a) the concentration of small particles and (b) the base 10 logarithm of the inertial number at $t=5.2\ \textrm {s}$ for a flow in which the large particles are more frictional than the fines. Here, as in figure 7, the parameters for each species are identical to those in table 1 except that $\mu _{s*}^{l}=1.2\mu _{s}$ and $\mu _{\infty }^{\nu }=0$ for both species. The inflow concentration is assumed to be a steady uniform solution (5.8) of the segregation equations assuming the parameters in table 3 and with $\overline {\varphi ^{s}}=0.5$. A movie of the full dynamics is available in the online supplementary movie 2.

Figure 11

Figure 9. Comparison of Tripathi & Khakhar's (2011) DEM simulations (markers) with theory (lines) for (a) the small particle concentration $\varphi ^{s}$ and (b) the downslope velocity $u$ at different depth-averaged small particle concentration $\overline {\varphi ^{s}}=0$, $30$, $50$, $70$ and $100\,\%$. The non-dimensional segregation constants are summarized in table 2 and the velocity is calculated using Tripathi & Khakhar's (2011) values of $\mu _s=\tan (20.16^{\circ })$ and $\mu _d=\tan (37.65^{\circ })$, while $I_0=0.5106$ is used to fit the steady-state 100 % small particle velocity profile.

Figure 12

Table 4. The fully coupled rotating drum simulations are performed with Barker & Gray's (2017) partially regularized friction law with parameters that match the steady-state DEM simulations of Tripathi & Khakhar (2011) shown in figure 9. The value of $\mu _{\infty }$ is chosen to ensure that the equations remain well-posed up to a maximum inertial number $I_{max}=16.20$, while $I_1$ is the minimum well-posed inertial number in the unregularized law. To handle the evolving free surface, the excess air segregates with a constant rate $f_{al}=f_{as}$ from the large and small particles and does not diffuse with them. The air phase is assumed to segregate upwards in the direction of the unit vector $\boldsymbol {k}$ along the $z$-axis, which this time is aligned with gravity.

Figure 13

Figure 10. Periodic motion of the bulk flow shown at $t=78.75\ \textrm {s}$ (a,c,e) and $t=80\ \textrm {s}$ (b,d,f), for (a,b) velocity magnitude in the rotating frame (i.e. minus the solid body rotation), (c,d) pressure and (e,f) base 10 logarithm of the inertial number $I$. The dashed lines in (e,f) indicate the height below which the high viscosity cutoff becomes active. The parameters used to compute the bulk flow, segregation and diffusion are summarized in tables 2 and 4. Supplementary movies 3–5 showing the full periodic solution are available in the online supplementary movies.

Figure 14

Figure 11. Fully coupled simulation of a bidisperse granular mixture in a square rotating drum using the parameters in tables 2 and 4, where the drum walls are of length 0.2 m: (a) plots $\varphi ^{s}$ at 10 s and (b–l) correspond to a further 6.25 s of rotation, or 5/8 of a full revolution, up to 78.75 s. A movie 6 is available in the online supplementary movies.

Figure 15

Figure 12. (a) Computed particle-size distribution after 78.1 s and (b) a comparable pattern formed in a rotating drum (Mounty 2007) with small white particles ($75\text {--}150\ \mathrm {\mu }\textrm {m}$) and large red particles ($400\text {--}500\ \mathrm {\mu }\textrm {m}$).

Figure 16

Figure 13. Integral $\mathscr {I}(t)$ of the small particle concentration difference between the current state and the state of one full revolution earlier, as a function of time and for four different mesh resolutions $N$ to demonstrate grid convergence of the numerical solution.

Barker et al. supplementary movie 1

Evolution of a granular flow front down a frictional plane inclined at ζ = 24◦. The bidisperse flow consists of a mixture of small and large particles that have identical rheological properties (listed in table 1) and no feedback from the evolving particle size distribution. The concentration of small particles is shown inside the granular material and the animation is stretched vertically in order to provide greater detail. The simulation is close to steady state by the end of the animation.

Download Barker et al. supplementary movie 1(Video)
Video 197.1 KB

Barker et al. supplementary movie 2

Animated contour plot of the concentration of small particles for a flow in which the large particles are more frictional than the fines. The inflow concentration is assumed to be a steady-uniform solution (5.8) of the segregation equations assuming the parameters in table 2 and with a depth-averaged concentration of small particles that is equal to one half. The frictional properties are described in detail in section 6.

Download Barker et al. supplementary movie 2(Video)
Video 192.7 KB

Barker et al. supplementary movie 3

Periodic motion of the bulk flow in a partially filled square rotating drum. The contours show the velocity magnitude in the rotating frame (i.e. minus the solid body rotation). The bulk flow is uncoupled from the segregation and the relevant parameters are given in table 1. The drum walls are of length 0.2 m.

Download Barker et al. supplementary movie 3(Video)
Video 4.3 MB

Barker et al. supplementary movie 4

Periodic motion of the bulk flow in a partially filled square rotating drum. The contours show the pressure. The bulk flow is uncoupled from the segregation and the relevant parameters are given in table 1. The drum walls are of length 0.2 m.

Download Barker et al. supplementary movie 4(Video)
Video 5.1 MB

Barker et al. supplementary movie 5

Periodic motion of the bulk flow in a partially filled square rotating drum. The contours show the base 10 logarithm of the inertial number. The bulk flow is uncoupled from the segregation and the relevant parameters are given in table 1. The drum walls are of length 0.2 m.

Download Barker et al. supplementary movie 5(Video)
Video 6.6 MB

Barker et al. supplementary movie 6

Numerical simulation of the evolving small particle concentration in a partially filled square rotating drum using the frictional properties in table 1 and the segregation parameters given in table 3. The drum walls are of length 0.2 m. The colour bar indicates that regions of purely small particles are displayed in red, and regions of purely large particles in blue. The air-grains interface is sharp, and the upper regions of air are made transparent.

Download Barker et al. supplementary movie 6(Video)
Video 5.6 MB