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Pre-asymptotic dispersion of active particles through a vertical pipe: the origin of hydrodynamic focusing

Published online by Cambridge University Press:  27 April 2023

Mingyang Guan
Affiliation:
Laboratory of Systems Ecology and Sustainability Science, College of Engineering, Peking University, Beijing 100871, PR China
Weiquan Jiang
Affiliation:
Macao Environmental Research Institute, Macau University of Science and Technology, Macao 999078, PR China
Bohan Wang
Affiliation:
Laboratory of Systems Ecology and Sustainability Science, College of Engineering, Peking University, Beijing 100871, PR China
Li Zeng
Affiliation:
State Key Laboratory of Simulation and Regulation of Water Cycle in River Basin, China Institute of Water Resources and Hydropower Research, Beijing 100038, PR China
Zhi Li
Affiliation:
Laboratory of Systems Ecology and Sustainability Science, College of Engineering, Peking University, Beijing 100871, PR China
Guoqian Chen*
Affiliation:
Laboratory of Systems Ecology and Sustainability Science, College of Engineering, Peking University, Beijing 100871, PR China Macao Environmental Research Institute, Macau University of Science and Technology, Macao 999078, PR China
*
†Email address for correspondence: gqchen@pku.edu.cn

Abstract

When motile algal cells are exposed to gyrotactic torques, their swimming directions are guided to form radial accumulation, well known as hydrodynamic focusing. The origin of hydrodynamic focusing from the effects of active swimming, ambient flow and particle anisotropy is elucidated in the present study on the pre-asymptotic dispersion of active particles through a vertical pipe. With an extension of the Galerkin method to pipe flows, time-dependent solutions directly from the Smoluchowski equation in the position and orientation space are derived by series expansions of spherical harmonics and Bessel functions. Ballistic and diffusive scaling laws are examined with the predominance of self-propelled swimming, and computation is validated against an explicit benchmark solution and Lagrangian particle simulation. In the limit of extreme shear, the competitive roles of shear dispersion and Brownian rotation are reflected concretely in the pre-asymptotic phase of hydrodynamic focusing. For flows with various shear strengths, a concentration peak in near-wall regions with a smooth transition to hydrodynamic focusing is illustrated with richer phenomena in upwelling and downwelling flows. A newly observed regime through a vertical pipe, named transient effective trapping, is revealed as a transitional mode towards hydrodynamic focusing. The pre-asymptotic approach to hydrodynamic focusing is elaborated intensively through extensive solutions of concentration moments and macroscopic transport coefficients characterised by swimming and flow Péclet numbers. The unique findings for the origin of hydrodynamic focusing could provide insight into related micro-algae reactor technology and contribute to flow control and biomass transfer in confined environments.

Information

Type
JFM Papers
Copyright
© The Author(s), 2023. Published by Cambridge University Press
Figure 0

Figure 1. Schematic of active particles in a downwelling flow through a vertical pipe. (a) Vertical pipe of radius $a^*$ with pointwise active particles initially oriented randomly and discharged uniformly at the origin point $O$ of the pipe. (b) Enlarged view of the point source of active particles. The swimming direction can be adjusted to be aligned with certain directions or distributed uniformly. (c) Descriptions of $\boldsymbol {p}$ in the cylindrical and spherical coordinate systems, where $\boldsymbol {p}$ is the swimming orientation with the polar angle $\theta$ and azimuthal angle $\phi$.

Figure 1

Figure 2. Illustration of transient shear–gyrotaxis interactions of active particles through a vertical pipe with the reflective boundary conditions. In an upwelling Poiseuille pipe flow at the left hand, the gyrotactic swimmer pointing inwards to the axis ($-{\rm \pi} <\phi <0$) is unstable since the joint efforts of the gravitational torque $T_G$ and viscous torque $T_\nu$ rotate the particles to move outwards and upwards. With the temporal evolution of gyrotaxis, the self-propelled particles would be trapped in the middle region away from the pipe wall before their eventual accumulation at the periphery of the pipe. In a downwelling Poiseuille pipe flow at the right hand, gyrotactic swimmers are instead stable with inward locomotion ($0<\phi <{\rm \pi}$) in specific shear regions. The competition between the pre-asymptotic near-wall peak and hydrodynamic focusing results in the rich phenomena observed in vertical pipe flows with different shear strengths. Transient effective trapping of pointwise active particles through a vertical pipe is revealed to be quite different from that in a horizontal flow as commonly observed.

Figure 2

Figure 3. The predominance of swimming is revealed during the approach to dispersion, in which the active swimming dispersion mechanism cooperates with the classical shear dispersion mechanism. Orientation-space-mean p.d.f.s $\langle P_0 \rangle _O$ of spherical active particles is shown with respect to $r$ without a background flow for different swimming Péclet numbers at (a) $t=0.5$, (b) $t=1$, and (c) $t=2$. All swimmers are initially randomly oriented and discharged with uniform distribution at the origin of the pipe. Common parameters: ${Pe} _f=0$, $D_t=0.01$, $\alpha _0=0$ and $\lambda =0$.

Figure 3

Figure 4. Distributions in the absence of background flow at $t=0.5$ as functions of swimming Péclet number: (a) number density, (b) wall-normal polarisation vector, and (c) wall-normal nematic order parameter. Pointwise active particles are initially oriented randomly and displaced uniformly at the origin of the pipe. Common parameters: ${Pe} _f=0$, $D_t=0.01$, $\alpha _0=0$ and $\lambda =0$.

Figure 4

Figure 5. General scaling laws without background flows: (a) MSD and (b) dispersivity. Ballistic and diffusive scaling laws are examined for the temporal evolution of the effective diffusivity, dedicating the initial regime, pre-asymptotic regime and dispersion regime. Numerically computed (lines) and benchmark (symbols) values of MSD and $D_T$ for active particles are illustrated with swimming Péclet numbers ${Pe} _s=0$ (circles), ${Pe} _s=0.1$ (triangles), ${Pe} _s=0.5$ (diamonds), ${Pe} _s=1$ (squares) and ${Pe} _s=2$ (inverted triangles). Computation of (2.20) and (2.18) collaborates perfectly with the benchmark solution (3.2) and (3.3), respectively. All swimmers are initially oriented randomly, and discharged with uniform distribution at the origin of the pipe. Common parameters: ${Pe} _f=0$, $D_t=10^{-4}$, $\alpha _0=0$ and $\lambda =0$.

Figure 5

Figure 6. Orientation-space-mean p.d.f.s $\langle P_0 \rangle _O$ of spherical active particles with respect to $r$ in weak shear as functions of time with different flow directions: (a) gyrotactic active particles ($\lambda =1$) in a downwelling Poiseuille flow; (b) non-gyrotactic active particles ($\lambda =0$) in a downwelling Poiseuille flow; and (c) gyrotactic active particles ($\lambda =1$) in an upwelling Poiseuille flow. The approach to hydrodynamic focusing of gyrotactic micro-organisms and uniformity of non-gyrotactic active particles is of particular interest. Peculiar concentration peaks in the middle region of upright pressure-driven flows are observed for only gyrotactic active flows. All swimmers are initially oriented randomly and discharged with uniform distribution at the origin of the pipe. Common parameters: ${Pe} _f=0.1$, ${Pe} _s=1$, $D_t=0$ and $\alpha _0=0$.

Figure 6

Figure 7. Orientation-space-mean p.d.f.s $\langle P_0 \rangle _O$ of spherical active particles with respect to $r$ in strong shear as functions of time with different flow directions: (a) gyrotactic active particles ($\lambda =1$) in a downwelling Poiseuille flow; (b) non-gyrotactic active particles ($\lambda =0$) in a downwelling Poiseuille flow; and (c) gyrotactic active particles ($\lambda =1$) in an upwelling Poiseuille flow. The flow strength and direction influence directly the concentration distribution of active particles, namely gyrotactic focusing on the axis in downwelling flows and wall accumulation at the periphery for upwelling cases. Interestingly, a natural transition from effective trapping towards hydrodynamic focusing is revealed inherently within such configurations. All swimmers are initially oriented randomly and discharged with uniform distribution at the origin of the pipe. Common parameters: ${Pe} _f=10$, ${Pe} _s=1$, $D_t=0$ and $\alpha _0=0$.

Figure 7

Figure 8. Evolutional origin of hydrodynamic focusing in an upwelling Poiseuille flow: (a) number density; (b) wall-normal polarisation vector; (c) wall-normal nematic order parameter; and (d) shear nematic alignment parameter. Pointwise active particles are initially oriented randomly and displaced uniformly at the origin of the pipe. Three typical time scales specified in different lines are $t=3$ (initial regime), $t=8$ (effective trapping in the pre-asymptotic regime), and $t=50$ (dispersion regime). Common parameters: ${Pe} _f=10$, ${Pe} _s=1$, $D_t=0$, $\alpha _0=0$ and $\lambda =1$.

Figure 8

Figure 9. Macroscopic transport characteristics as functions of flow Péclet number under the effect of downwelling shear flows: (a) drift, (b) dispersivity, and (c) skewness. By fixing ${Pe} _s$ as unity, the flow strength significantly enhances the Taylor dispersion of active particles, with the combined action of active dispersion. Persistent asymmetries are reported during the pre-asymptotic regime. Interestingly, transitions from positive to negative skewness are illustrated in weak shear for the interchanges of various balance mechanisms. All gyrotactic swimmers are initially oriented randomly and discharged with uniform distribution at the origin of the pipe. Common parameters: $D_t=0$, $\alpha _0=0$ and $\lambda =1$.

Figure 9

Figure 10. Effect of particle anisotropy in an upwelling flow. Shear alignment and vortical rotation are the main mechanisms of ellipsoidal active particles, giving rise to the appreciable phenomena of enhanced upstream rheotaxis, effective trapping and dispersion. Times: (a) $t=1$, (b) $t=2$, (c) $t=4$, and (d) $t=10$. Pointwise gyrotactic swimmers are initially oriented vertically upwards and displaced uniformly at the origin of the pipe. Common parameters: ${Pe} _f=1$, $D_t=0$, ${Pe} _s=1$ and $\lambda =1$.

Figure 10

Figure 11. Distributions in an upwelling Poiseuille flow as functions of particle anisotropy: (a) number density; (b) wall-normal polarisation vector; (c) wall-normal nematic order parameter; and (d) shear nematic alignment parameter. The time specified corresponds to the effective trapping of elongated active rods observed in the pre-asymptotic regime at $t=4$. Pointwise active particles are initially oriented randomly and displaced uniformly at the origin of the pipe. Common parameters: ${Pe} _f=1$, $D_t=0$, ${Pe} _s=1$ and $\lambda =1$.

Figure 11

Figure 12. Temporal evolution of macroscopic transport characteristics as a function of particle anisotropy in upwelling shear flows: (a) drift, (b) dispersivity, and (c) skewness. Different aspect ratios ($\alpha _0=0$, 0.5 and $1$) of spherical and elongated gyrotactic swimmers are investigated under the effect of shear alignment and vortical rotation. The dominance of shear-induced alignment over vortical rotation leads to upstream swimming during the pre-asymptotic regime. The persistent effective trapping and enhanced dispersion of elongated particles could contribute to cell separation and cultivation. All pointwise gyrotactic swimmers are initially oriented randomly and discharged with uniform distribution at the origin of the pipe. Common parameters: ${Pe} _f=1$, $D_t=0$, ${Pe} _s=1$ and $\lambda =1$.

Figure 12

Figure 13. Comparison of Lagrangian particle simulation (symbols) and theoretical (lines) first moment $M_1$, and MSD $\sigma ^2$, with red and blue for non-gyrotactic ($\lambda =0$) and gyrotactic ($\lambda =1$) active particles, respectively. In this downwelling Poiseuille flow, pointwise swimmers are initially oriented vertically upwards and displaced uniformly at the origin of the pipe. A total of $10^5$ particles are released for each run, with time step $10^{-3}$. Common parameters: ${Pe} _f=1$, ${Pe}_s=1$ and $D_t=0$.