
Citation: | S. Barik, and D. C. Dalal, Analytical solution for concentration distribution in an open channel flow with phase exchange kinetics, Acta Mech. Sin. 38, 321506 (2022), |
Solute transport in a flowing fluid is an important topic of research in modern times and it has wide applications in diverse fields such as biology [1-3], environment fluid mechanics [4-10], and chromatography [11], etc. Among the many applications in environmental processes such as atmosphere, estuaries, and wetlands, it is important to find the dispersion phenomena for pollutant transport in river, which has important applications for environmental risk assessment [12], where actual prediction of reactive solute is of under concern.
Theoretically as well as experimentally, the longitudinal dispersion of an inert (i.e., non-adsorbing) solute in an incompressible fluid flow through a circular tube was first studied by G. I. Taylor [13]. He showed that velocity difference in the fluid layer across the tube enhanced the overall diffusivity of the solute. The effective diffusion is called as Taylor dispersion. He found the dispersion coefficient (
The idea of Taylor on the solute dispersion extensively studied by many researchers. Numerical attempts include the study of Takahashi et al. [15], Stokes and Barton [16], Ekambara and Joshi [17], Lau and Ng [18], Mondal et al. [19], Dhar et al. [20], etc. Besides researchers also adopted different analytical methods to analyse the solute dispersion that includes the Aris's moment method [14, 21], mean concentration expansion method by Gill [22-26], multi-scale method of homogenization [27-31], and delay-diffusion method [32].
Effect of partitioning between phases on axial dispersion behaviour was initially analysed by Westhaver [33]. Since the pioneering work of Taylor [13], the study of solute dispersion has been extended in various ways to account for partitioning effects [34]. Shankar and Lenhoff [11] studied the gas chromatography in a coated tube within a retentive layer. Phillips and Kaye [35] studied the effect of reversible phase exchange on the solute transport in a two-phase system. Ng and Yip [36] presented a theory for the transport in open-channel flow of a chemical species under the influence of kinetic sorptive exchange between phases that are dissolved in water and sorbed onto suspended sediments. Solute transport in oscillatory Couette flow through two parallel plate with sorptive boundaries has been analysed by Ng and Bai [37]. They showed that if the phase exchange is sufficiently kinetic, the dispersion coefficient can be much higher than its inert counterpart. In his works, Ng [38, 39] has studied the effect of reversible phase exchange kinetics as well as wall absorption on dispersion coefficients in oscillatory flows. They have derived the higher-order dispersion coefficients, which arise from the combined effects of phase exchange kinetics and bed absorption. They showed that the higher-order dispersion coefficients can be comparable with their leading order counterparts in the presence of kinetic sorptive exchange with the bed.
Many literature are available on solute transport, where efforts was only made for analysing the mean concentration distribution [40-46] rather than two-dimensional transverse concentration distribution. Some of the environmental or industrial processes, the two-dimensional concentration distribution is equally important with longitudinal mean concentration distribution. Earlier, researchers believed that cross-sectional concentration variation was negligible for the Taylor dispersion stage of the transport process and mean concentration was enough to demonstrate the solute dispersion process. But, the study of Wu and Chen [47, 48] reveals that transverse variation is significant for a longer period of time. They derived the analytical expression for the two-dimensional transverse concentration distribution in steady flows using Mei's homogenization technique [49]. They also analysed the transverse uniformity of concentration cloud for laminar steady flows and proposed a time scale
The main objectives of this work include a multi-scale analysis for the concentration distribution in an open channel flow with sorptive channel bed, finding the analytical expressions for dispersion coefficient and both mean and two-dimensional real concentrations up to second-order approximation, observe the effects of phase exchange kinetics on dispersion coefficient and two-dimensional concentration distribution, discuss the effect of phase exchange kinetics on uniformity in two-dimensional concentration over the channel cross-section.
We study a laminar, unidirectional, fully developed, open channel flow, where the width between free surface and channel bed is
where
Let us release the solute of mass
where
where
where
where
The solute transport problem can be written as
where
The initial and boundary conditions are taken as
and
where
To apply multi-scale method at first we have to choose different scales for length and time. For length we have chosen two different scales as
Their ratios are
where
Now we introduce the dimensionless parameters as
where
As per the timescale we have introduced the order of
Then governing equation and boundary conditions can be written in dimensionless form as
The velocity profile is written in dimensionless form as
The homogenization technique of Mei et al. [49] is used to carry out the asymptotic analysis. The mobile and immobile phase concentrations
and
Let us introduce the fast, medium and slow time variables, based on three time scales
According to the chain rule we can write,
Substituting Eqs. (16)-(18) into Eqs. (12)-(14) results in
For leading order (
The general solution of Eq. (22) becomes
The depth of the channel is considered to be narrow enough so that transverse diffusion takes place almost immediately (with in the first time scale) after the release. It is observed from the equation that the numerically value of series part decreases exponentially with fast time variable, and it become insignificant for
So
For first order (
The time scale
Taking a section average of Eq. (31) w.r.t.
where
Subtracting Eq. (32) from Eq. (31), we get
These equation suggest the following substitutions
where
with the following conditions
and
For second order (
The time scale
Taking a section average of Eq. (43) w.r.t.
The second, third, and fourth terms of L.H.S of Eq. (44) can be found using Eqs. (32), (34), (35), and (39) as
and
Using Eqs. (45)-(47) in Eq. (44) we get
Multiplying Eqs. (32) and (48) by
Rewriting Eq. (49) in original time variable as
where
The range of validity of
Without phase exchange effect the above range becomes,
Solving the two system of Eqs. (36)-(39), we have
and using Eqs. (15) and (53) one can find
Let us use the transformations
Using the initial and boundary conditions given in Eqs. (6) and (9), the solution of Eq. (56) can be found as
Eliminating
After substitute the required terms of Eq. (58) one can get
and from Eq. (42) one can get
In the above equations one can neglect the first term associated with
where
and
On solving Eqs. (63)-(66) one can get
and
In a similar manner we can obtain the terms
which are same to those obtained in the work of Wu and Chen [48].
In this section we have discussed about Taylor dispersivity, distributions of mean concentration and of two-dimensional transverse concentration. Taylor dispersivity and the concentrations depend on the parameters
The first term on R.H.S of the effective dispersion coefficient
The analytical expression for mean concentration can be found from Eqs. (16) and (57) in a new
From Eq. (16), the two-dimensional transverse concentration distribution up to second order is obtained as
As we have not come across any literature that can be used directly to compare the two-dimensional concentration profile of the present problem, so results of the present study for
The explicit form of the dispersion coefficient can be derived from Eqs. (54), (55), and (71) as
which is identical with the steady state dispersion coefficient obtained by Ng [39] in his study. In the inert case (when
which is same as that obtained by Wu and Chen [48].
Effects of partition coefficient (
From Eq. (74), the gradient of
which is always positive and is large for small
The values of maximum
Max{ | |||
---|---|---|---|
0.1 | 1.5490 | 0.5154 | 81.3225 |
1 | 0.2194 | 0.6588 | 11.5185 |
10 | 0.0981 | 1.2386 | 5.1502 |
100 | 0.0886 | 1.4317 | 4.6515 |
0.0876 | 1.4557 | 4.5990 |
From Eq. (72), the explicit form of the mean concentration distribution can be written as
The present study is not intended to focus on the longitudinal skewness of concentration cloud at initial times. The expression for mean concentration becomes exactly similar to that of Taylor dispersion model. The expression of mean (Eq. (78)) can give an excellent result after some initial time when the longitudinal skewness completely dies out.
Longitudinal distributions of mean concentration in the channel are shown in Fig. 4. Figure 4a shows the distribution curves of mean for different values of
0.1 | 0.5154 | 1.6528 | 0.8238 | 0.3190 | 0.2369 | 0.2267 | 0.2442 | 0.3820 | 0.5223 | 0.8395 |
1 | 0.6588 | 1.9868 | 1.6313 | 0.8666 | 0.6497 | 0.6081 | 0.6163 | 0.8027 | 0.9767 | 1.3253 |
10 | 1.2386 | 2.0326 | 1.9389 | 1.4404 | 1.1011 | 0.9861 | 0.9056 | 0.9892 | 1.1276 | 1.4368 |
The two-dimensional concentration distributions for mobile and immobile phases can be written explicitly up to second order as
Concentration contour plots are given in Figs. 5 and 6, which demonstrate the effects of reversible phase exchange. Initially, the solute is introduced at
Variation of immobile phase concentration distribution is depicted in Fig. 7. As a comparison, mean concentration in the mobile phase is shown in the figure. Figure 7 reveals that increase in retention parameter always increases the immobile flow concentration as retention capacity of the channel bed increases with the increase in
In this study an indicator
which measures the two-dimensional concentration variation rate over the channel cross-section against the center of solute concentration.
The axial distribution of the two-dimensional concentration variation rate is presented in Fig. 8. From Fig. 8a it can be seen that the variation rates are exactly similar around the vertical axis for the inert case and with the increase of time the maximum variation rates moves away from the solute centroid. Effects of retention parameter on concentration variation rate are plotted in Fig. 8b-d. Figures show that for
0.1 | 40.32 | 35.94 | 30.97 | 30.42 | 30.69 | 31.05 | 32.22 | 39.82 | 49.62 | 72.45 |
1 | 40.32 | 39.74 | 36.55 | 33.64 | 35.33 | 37.47 | 43.12 | 62.78 | 76.52 | 98.33 |
10 | 40.32 | 40.31 | 40.22 | 41.26 | 44.94 | 48.18 | 54.88 | 72.71 | 84.41 | 103.34 |
15 | 40.32 | 40.33 | 40.41 | 42.08 | 45.94 | 49.16 | 55.72 | 73.20 | 84.77 | 103.55 |
The solute dispersion in an open channel flow that involves phase exchange between mobile and immobile phases is studied using multi-scale method of homogenization. Effects of retention parameter and phase exchange kinetics on dispersion coefficient, mean and two-dimensional real concentrations are discussed. Analytical solutions for mean and two-dimensional concentrations are obtained up to second order approximation. The pattern of two-dimensional real concentration distribution and its uniformity over the cross-section of the channel are also discussed in this study. An indicator for characterizing the two-dimensional concentration variation rate is adopted, which measures the variation rate of concentration over the cross-section of the channel.
It is noted that as
In this paper, we have concentrated mainly on analytical developments. We have verified our results with the existing results for a particular case. Our objective is to visualize the long time evolution pattern of the concentration distribution. Comparison with numerical results would be a very good addition. In future one can study this problem numerically to verify the adaptability of the homogenization results in the transient regime. Though our study provides the long time evolution pattern of solute concentration distribution, further analysis can be made on the early time evolution.
The authors would like to express sincere thanks to two referees for providing suggestions for improvement of the paper.Executive Editor: Shijun Liao
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Max{ | |||
---|---|---|---|
0.1 | 1.5490 | 0.5154 | 81.3225 |
1 | 0.2194 | 0.6588 | 11.5185 |
10 | 0.0981 | 1.2386 | 5.1502 |
100 | 0.0886 | 1.4317 | 4.6515 |
0.0876 | 1.4557 | 4.5990 |
0.1 | 0.5154 | 1.6528 | 0.8238 | 0.3190 | 0.2369 | 0.2267 | 0.2442 | 0.3820 | 0.5223 | 0.8395 |
1 | 0.6588 | 1.9868 | 1.6313 | 0.8666 | 0.6497 | 0.6081 | 0.6163 | 0.8027 | 0.9767 | 1.3253 |
10 | 1.2386 | 2.0326 | 1.9389 | 1.4404 | 1.1011 | 0.9861 | 0.9056 | 0.9892 | 1.1276 | 1.4368 |
0.1 | 40.32 | 35.94 | 30.97 | 30.42 | 30.69 | 31.05 | 32.22 | 39.82 | 49.62 | 72.45 |
1 | 40.32 | 39.74 | 36.55 | 33.64 | 35.33 | 37.47 | 43.12 | 62.78 | 76.52 | 98.33 |
10 | 40.32 | 40.31 | 40.22 | 41.26 | 44.94 | 48.18 | 54.88 | 72.71 | 84.41 | 103.34 |
15 | 40.32 | 40.33 | 40.41 | 42.08 | 45.94 | 49.16 | 55.72 | 73.20 | 84.77 | 103.55 |
Max{ | |||
---|---|---|---|
0.1 | 1.5490 | 0.5154 | 81.3225 |
1 | 0.2194 | 0.6588 | 11.5185 |
10 | 0.0981 | 1.2386 | 5.1502 |
100 | 0.0886 | 1.4317 | 4.6515 |
0.0876 | 1.4557 | 4.5990 |
0.1 | 0.5154 | 1.6528 | 0.8238 | 0.3190 | 0.2369 | 0.2267 | 0.2442 | 0.3820 | 0.5223 | 0.8395 |
1 | 0.6588 | 1.9868 | 1.6313 | 0.8666 | 0.6497 | 0.6081 | 0.6163 | 0.8027 | 0.9767 | 1.3253 |
10 | 1.2386 | 2.0326 | 1.9389 | 1.4404 | 1.1011 | 0.9861 | 0.9056 | 0.9892 | 1.1276 | 1.4368 |
0.1 | 40.32 | 35.94 | 30.97 | 30.42 | 30.69 | 31.05 | 32.22 | 39.82 | 49.62 | 72.45 |
1 | 40.32 | 39.74 | 36.55 | 33.64 | 35.33 | 37.47 | 43.12 | 62.78 | 76.52 | 98.33 |
10 | 40.32 | 40.31 | 40.22 | 41.26 | 44.94 | 48.18 | 54.88 | 72.71 | 84.41 | 103.34 |
15 | 40.32 | 40.33 | 40.41 | 42.08 | 45.94 | 49.16 | 55.72 | 73.20 | 84.77 | 103.55 |