1. Introduction
Dispersion is a fundamental transport process in engineering and environmental systems, including rivers, estuaries and coastal zones (Brenner & Edwards Reference Brenner and Edwards1993). For dispersion in pipe Poiseuille flows, as originally examined by Taylor (Reference Taylor1953), transverse diffusion within the confined cross-section interacts with shear to produce an enhanced longitudinal diffusion. Taylor (Reference Taylor1954) modelled solute dispersion in fully developed turbulent pipe flows using a one-dimensional effective diffusion equation, with the general logarithmic velocity and Reynolds-analogy-based eddy diffusivity. Despite its simplicity, this is still the most widely used model for scalar (say heat or solute) in flows, with applications in modelling contaminant dispersion, heat transfer and other related transport phenomena (Taylor Reference Taylor1954; Elder Reference Fischer1959; Fischer Reference Fischer1966; Chatwin Reference Chatwin1970; Sayre Reference Sayre1975; Fischer Reference Follett, Hays and Nepf1979; Barton Reference Barton1983a ; Croze, Bearon & Bees Reference Croze, Bearon and Bees2017; Guo et al. Reference Hanjalić and Launder2021; Guan et al. Reference Guan, Jiang, Wang, Zeng, Li and Chen2024; Barik & Tsai Reference Barik and Tsai2025), with long history. Importantly, the enduring relevance of such models lies in their strong foundation of experimental support (Kalinske & Pien Reference Kendall and Stuart1944; Pasquill & Taylor Reference Pirozzoli1997; Min, Abernathy & Lundblad Reference Murphy, Ghisalberti and Nepf2002; Murphy, Ghisalberti & Nepf Reference Nepf and Ghisalberti2007; Guo, Jiang & Chen Reference Guo, Jiang, Chen, Li, Alharbi and Wakeel2020). In essence, dispersion arises from the interplay between longitudinal advection, which varies with cross-sectional position, and diffusion induced by turbulence or Brownian motion. Taylor assumed a simplified asymptotic form when the drift velocity is modelled as a stationary random function of time, within a reference frame moving at the mean flow velocity (Taylor Reference Taylor1953, Reference Taylor1954; Batchelor Reference Batchelor1957). Turbulent shear flows in an open channel hence introduce an additional dimension that facilitates direct examination of the assumptions underlying Taylor’s turbulent dispersion theory (Elder Reference Fischer1959).
Fluid motion in nature is typically turbulent, causing passive or active matter to disperse more rapidly through unsteady and random processes compared to laminar flows (Yang et al. Reference Yang, Chen, Verzicco and Lohse2020; Bo et al. Reference Bo, Ralston, Geyer and McWilliams2024; Ouyang et al. Reference Park and Hwang2025). Across different scales of turbulent flows, the centroid of a mass cloud can deviate markedly from the Lagrangian path of fluid particles because of large-scale eddies (Xia et al. Reference Xia, Francois, Punzmann and Shats2013). Based on the framework of Stone & Brenner (Reference Stone and Brenner1999) that extended Taylor’s dispersion solution to include perturbed axial velocity variations, Samuel et al. (Reference Samuel, Chang, Ma and Santiago2025) explored the transient dispersion behaviour of a solute in coupled electro-osmotic and pressure-driven flows, and proposed optimisation strategies that effectively reduce dispersion across time scales. Nonetheless, classical dispersion theories, notably those developed by Taylor (Reference Taylor1954), Batchelor (Reference Batchelor1957) and Brenner & Edwards (Reference Brenner and Edwards1993), rely on long-time asymptotic assumptions and cross-sectional averaging. Generally, transport and dispersion rates are largely influenced by physicochemical properties of contaminants, as well as statistical characteristics of turbulent flows in water bodies. However, relationships between phenomenological parameters and dispersion processes are highly complex (Zeng, Jiang & Pedley Reference Zeng, Jiang and Pedley2022; Guan et al. Reference Guan, Zeng, Jiang, Guo, Wang, Wu, Li and Chen2023; Wang et al. Reference Wang, Wu, Zhang, Wang and Chen2024, Reference Wang, Jiang, Zeng and Chen2025a ; Ding Reference Ding, Hunt, McLaughlin and Woodie2025; Zeng et al. Reference Zeng, Jiang, Guan, Lee and Chen2025). Due to the insufficient understanding of these interactions (Vilquin et al. Reference Vilquin, Bertin, Raphaël, Dean, Salez and McGraw2023; Aquino Reference Aquino2024), Taylor’s long-time criteria for predicting the macroscopic dispersion rates require improvement, and justifications for streamwise dispersion models are in need (Smith Reference Smith1982b ).
The regulation of harmful contaminants has become increasingly critical to prevent concentrations from exceeding safe thresholds (Li et al. Reference Liang and Wu2024). As industrial, agricultural and domestic waste generation continues to grow, the margin for error in monitoring and treatment systems is narrowing (Christou et al. Reference Christou2024). A central challenge lies in the safe transport and mitigation of pollutants, which include radioactive waste, effluents from power plants and agricultural pesticides (Maggi, Tang & Tubiello Reference Mashayekhpour, Marchioli, Lovecchio, Lay and Soldati2023). Effective pollution control and sustainable water supply management therefore require reliable strategies to limit the spread of such substances. These concerns highlight the importance of developing a quantitative understanding of dispersion processes in both natural and engineered turbulent flows.
Considerable attention has been devoted to the transport of passive scalars through open channel turbulence (Pirozzoli Reference Pope2023), with particular emphasis on sediment transport (DiBenedetto, Clark & Pujara Reference Ding2022; Zeng et al. Reference Zeng, Jiang, Wang, Zeng, Guan, Li and Chen2024) and mass and momentum exchanges at the free surface (Mashayekhpour et al. Reference Min, Abernathy and Lundblad2019; von Wenczowski & Manhart Reference von Wenczowski and Manhart2025). In recent decades, research on turbulent dispersion in open channel flows has intensified, particularly in relation to the effects of submerged and emergent vegetation (Nepf Reference Öttinger2012; Sehat et al. Reference Sehat, Abdolahpour, Jamali and Ghisalberti2023; Park & Nepf Reference Pasquill and Taylor2025), solute shape and size (Sanness Salmon et al. Reference Sanness Salmon, Baker, Kozarek and Coletti2023), and spatial arrangement of aquatic plants (Park & Hwang Reference Park and Nepf2019; Sehat et al. Reference Sehat, Abdolahpour, Jamali and Ghisalberti2023) – features commonly observed in natural water bodies.
Extensive experimental and computational efforts also focused on understanding turbulent dispersion with inhomogeneity and anisotropy (del Refugio Cabañas-Mendoza et al. Reference DiBenedetto, Clark and Pujara2024). Since in most practical flows the scale of turbulent eddies is significantly smaller than that of the bulk flow, it is reasonable to resort to continuum modelling for tractable solutions (Shirolkar, Coimbra & Queiroz McQuay Reference Shirolkar, Coimbra and Queiroz McQuay1996). Widely used turbulence models are based on Reynolds-averaged and/or phase-averaged Navier–Stokes equations, together with empirical closure models (Hanjalić & Launder Reference Jiang and Chen2022). The development of these models has been guided by experimental benchmarks, ranging from early measurements of diffusion in turbulent streams (Kalinske & Pien Reference Kendall and Stuart1944) and the vertical structure of stratified lakes (Min et al. Reference Murphy, Ghisalberti and Nepf2002), to atmospheric boundary-layer dispersion studies (Pasquill & Taylor Reference Pirozzoli1997). Such controlled experiments provide particle statistics under well-defined boundary conditions in both non-reacting and reacting scenarios (Snyder & Lumley Reference Snyder and Lumley1971; Wells & Stock Reference Wells and Stock1983), and continue to inform models that integrate flow properties and boundary effects, e.g. for predicting drag coefficients in turbulent environments (Liu & Wang Reference Maggi, Tang and Tubiello2024; Zhang et al. Reference Zhang, Cheng, Hassan, Wang and Wu2024).
From an analytical perspective, Aris (Reference Aris1956) formalised the method of moments for Taylor dispersion, defining the long-time effective diffusivity (termed dispersivity) as half the rate of change of the axial variance. Barton (Reference Barton1983b ) provided explicit solutions for the first few moments using separation of variables, making Taylor–Aris moment analysis quite prevalent in dispersion studies. Jiang & Chen (Reference Jiang and Chen2018) employed the solutions of moments to accurately determine the coefficients of Gill’s dispersion model (Gill & Sankarasubramanian Reference Gill and Sankarasubramanian1971), allowing for systematic programming of higher orders and extension to solve relevant models. Recently, the moment method has been extended to include applications of reactive dispersion with adsorption and desorption boundaries (Zhang, Hesse & Wang Reference Zhang, Hesse and Wang2017; Jiang et al. Reference Kalinske and Pien2022; Wang et al. Reference Wang, Jiang, Chen and Tao2022). Nonetheless, at short times, the statistical properties of the mean concentration primarily reflect artefacts introduced by the averaging process (Smith Reference Smith1982b ). For instance, dispersivity can become negative in certain regimes due to a decreasing rate of variance, as shown in reversing flows of oscillatory currents (Smith Reference Smith1982a ). Negative dispersivity is sometimes deemed physically unrealistic when Taylor dispersion arising from shear is interpreted as a mixing process, especially in the context of turbulent flows (Yasuda Reference Yasuda1984). In a similar manner, the classical drift–diffusion models proposed by Gill (Reference Guan and Chen1967) and Chatwin (Reference Chatwin1970), whether employing constant or time-dependent dispersion coefficients, relied on the flawed average statistics to derive various series expansions. Clearly, the use of average statistics from coarse-grained concentration profiles can lead to the loss of critical information needed for reconstruction of local concentration distributions and other practical predictions. Consequently, the models cannot be regarded as quantitatively valid in general for short times.
Streamwise dispersion models with accurate local input have potential to provide comprehensive solutions for the complete characterisation of local concentration. DeGance & Johns (Reference DeGance and Johns1980) proposed a theoretical justification for Gill’s model by addressing the same problem through an expansion of the local concentration in Hermite polynomials along the streamwise direction. Using approximations for the higher-order coefficients of Bessel functions in the series expansion of local concentration, Yu (Reference Yu1981) proposed an effective solution for transient dispersion in pipe flows. Subsequently, Smith (Reference Smith1982b ) presented a Gaussian approximation for local concentration distributions at early times, majorly based on the short-time approximate source solution of Saffman (Reference Saffman1960) and long-time dispersion solution of Taylor (Reference Taylor1953). More recently, Guan & Chen (Reference Guan, Jiang, Tao, Chen and Lee2024) provided a rigorous justification and physical interpretation for the series expansions of local moments in a pipe Poiseuille flow, developing a general streamwise dispersion model from a Lagrangian perspective that captures Taylor dispersion with multi-scale effects. To accurately characterise the whole process, it is essential to define the local statistics, establish their relation to the asymptotic cross-sectional means, and identify the dominant physical mechanisms.
Guan & Chen (Reference Guan, Jiang, Tao, Chen and Lee2024) demonstrated that when a neutrally buoyant, diffusible solute is released into solvent flowing through a tube, dispersion along each streamline can be effectively described in a reference frame moving with the local streamwise velocity. In this Lagrangian system, the evolution of the solute appears as if governed by a time-dependent anisotropic diffusivity tensor. The proposed convection transformation inherently yields three characteristic regimes of dispersion, determined by the dimensionless product of the Péclet number
$\textit{Pe}$
– which quantifies the ratio of advective transport to diffusion – and time
$t$
. At short times, dispersion is dominated by isotropic diffusion. For sufficiently long times, an enhanced streamwise diffusivity emerges, consistent with the classical Taylor dispersion. By employing eigenfunction expansions and asymptotic matching, a general streamwise dispersion model unifying short- and long-time behaviours is developed and analytically solved. The model captures several interesting phenomena through pipe Poiseuille flows, including pronounced peaks in solute concentration, significantly amplified local dispersivity and asymmetric spreading patterns. It is now performed for the case of a turbulent open channel flow for a refined characterisation of dispersion dynamics beyond conventional models.
One of the earliest analytical extensions to turbulent open channel flows was made by Elder (Reference Fischer1959), who adapted Taylor’s framework and calibrated the longitudinal diffusivity based on experimental observations. Building on this, Chatwin (Reference Chatwin1970) used long-time asymptotic expansions to examine second- and third-order average moments, showing close alignment with numerical results. Barton (Reference Barton1983b ) advanced the moment method by deriving explicit formulas for average moments in turbulent open channel flows. In parallel, Fischer demonstrated the applicability of Fickian turbulent diffusivity coefficients, lending support to simplified drift–diffusivity models in natural water bodies (Fischer Reference Fischer1966, Reference Fischer1976, Reference Follett, Hays and Nepf1979). Temporal evolution of dispersion has also been explored: Sayre (Reference Sayre1975) separated dispersion into initial and asymptotic phases, while Sullivan (Reference Sullivan1971) identified three key stages for a two-dimensional turbulence through experimental and numerical investigations. More recently, Guo et al. (Reference Hanjalić and Launder2021) applied Gill’s generalised model to analytically characterise dominant time scales of solute transport. For more realistic applications, Barik & Tsai (Reference Barik and Tsai2025) introduced a modified turbulent diffusivity model, including reversible and irreversible reactions. To the best of our knowledge, existing theoretical studies on Taylor dispersion in turbulent open channel flows have largely focused on the asymptotic regime, without providing reliable predictions of either average or local concentration distributions.
This work seeks to elucidate the general mechanism of streamwise dispersion and to develop a unifying dispersion model for predicting local concentration in turbulent open channel flows. Section 2 introduces the fundamental transport problem, introducing definitions and analytical solutions for both local and average moments. In § 3, the diffusive framework is formally justified through the asymptotic analysis and the convective transformation. Taylor’s dispersion model is then generalised to incorporate transient local moments, allowing for a systematic derivation of local concentration distribution. Section 4 illustrates several intriguing results, including the overshoot in local dispersivity, the emergence of skewed long tails in mean concentration profiles, and the formation of island-shaped accumulation zones near the free surface. To our knowledge, this is the first analytical derivation of local distributions in turbulent channel flows that accurately reproduces the vertical concentration structure. Finally, § 5 concludes with a summary of findings.
2. Formulation of the basic transport problem
2.1. Problem description
We study the soluble matter dispersing in a turbulent open channel flow, as shown in figure 1. By assuming that the mass and momentum transport in turbulent flows can be treated analogously (Reynolds’ analogy) and that isotropic turbulent diffusion can be well modelled using an eddy diffusivity
$K^\ast$
that varies with depth (Taylor Reference Taylor1954), a simple yet pedagogically significant and theoretically useful model for turbulent open channel flows is obtained (Elder Reference Fischer1959; Chatwin Reference Chatwin1970; Barton Reference Barton1983a
). In dimensional form, the Reynolds-averaged convection–diffusion equation is given by
where
$C^*$
is the concentration of solute,
$t^*$
is the time,
$u^*$
is the flow velocity,
$\xi ^*$
is the longitudinal coordinate, and
$z^*$
is the vertical coordinate. Dimensionless parameters are introduced as
where
$h^*$
is the height of the channel,
$Q^*$
is the total mass per unit length,
$\bar {K}^*$
is the average diffusivity,
$\kappa$
is the von Kármán constant, and
$u_\tau ^*$
is the friction velocity. The average turbulent diffusivity
$\bar {K}^*$
is defined through the dimensional eddy diffusivity
$K^*=\kappa h^* u_\tau ^* (1-z^*/h^*) z^*/h^*$
as
and the dimensional average velocity
$\bar {u}^*$
is defined by
Note that the eddy diffusivity
$K$
is generally a function of both space and time, as it reflects the underlying eddy structures, which can evolve temporally and vary spatially. Different assumptions regarding the form of
$K$
lead to different modelling approaches, each involving trade-offs between empirical observations and theoretical formulation (Pope Reference Refugio Cabañas-Mendoza, Olguín, Sánchez-Galván, Melo and Barrientos2001). The dimensionless velocity and turbulent diffusivity are adopted as (Elder Reference Fischer1959; Fischer Reference Fischer1966, Reference Fischer1976, Reference Follett, Hays and Nepf1979; Chatwin Reference Chatwin1970; Sayre Reference Sayre1975; Barton Reference Barton1983a
; Guo et al. Reference Hanjalić and Launder2021)
Despite its simplicity, the log-law turbulent velocity profile combined with a basic eddy diffusivity formulation remains a classical and widely used model for turbulent dispersion. This approach has a long history of use in both theoretical and applied studies (Taylor Reference Taylor1954; Elder Reference Fischer1959; Fischer Reference Fischer1966, Reference Fischer1976, Reference Follett, Hays and Nepf1979; Chatwin Reference Chatwin1970; Sayre Reference Sayre1975; Barton Reference Barton1983a
; Guo et al. Reference Hanjalić and Launder2021; Barik & Tsai Reference Barik and Tsai2025). The moment theory and diffusive formulation developed hereafter are general and can readily accommodate alternative or more accurate eddy diffusivity profiles (Ghisalberti & Nepf Reference Gill2005; Nepf & Ghisalberti Reference Nepf2008; Liang & Wu Reference Liu and Wang2014; Follett, Hays & Nepf Reference Ghisalberti and Nepf2019). In this sense, the present choice serves primarily as a canonical case that highlights the dominant physical mechanisms while allowing straightforward extensions. These idealisations not only reflect dominant physical mechanisms, but also serve to make the problem analytically tractable and facilitate comparisons with canonical models. Specifically, in a two-dimensional coordinate system (where
$\xi$
and
$z$
denote the dimensionless longitudinal and vertical coordinates, respectively), the governing equation of concentration
$C$
becomes
Sketch for streamwise dispersion of soluble matter with eddy diffusion in a fully developed turbulent open channel flow following von Kármán’s logarithmic law from an initial line source discharge.

The initial condition reads
where
$\mathcal{C}^0$
is the initial concentration distribution corresponding to
Boundary conditions are employed as
2.2. Solutions of local and average moments
Since our focus is on the streamwise dispersion of a solute, an efficient way to characterise its evolution is through the local and average moments of the concentration. The moment method offers an analytical framework to track the centre of mass, the variance and higher-order structures of the concentration distribution over time. This approach generalises Taylor’s classical theory by incorporating spatial variations and depth-dependent diffusivity profiles. Building on the mathematical equivalence between moments and cumulants, we will later formulate a streamwise dispersion model in terms of local statistics. The analytical procedures for deriving these moment solutions are presented in this subsection.
Local moments of concentration can be defined as
Assuming that the concentration and its derivatives decay sufficiently rapidly as
$\left |\xi \right |\rightarrow \infty$
(e.g. exponentially), the boundary terms arising from integration by parts vanish, i.e.
Then
$C_n$
possesses analytical solutions of the following problem (Aris Reference Aris1956; Barton Reference Barton1983a
,
Reference Bartonb
):
\begin{equation} \left .\begin{array}{c} \dfrac {\partial C_n }{\partial t } - \dfrac {{\partial } }{\partial {{z }}} \left (K(z) \dfrac {{\partial }C_n }{\partial {{z }}} \right ) = n(n-1)\, K(z)\, C_{n-2}+n\, \textit{Pe} u(z)\, C_{n-1},\\[9pt] \left .C_n\right |_{t=0}=\mathcal{C}_n^0,\\[9pt] {{\left . \left (K(z)\dfrac {\partial C_n }{\partial z }\right ) \right |}_{z =0}} ={{\left . \left (K(z)\dfrac {\partial C_n }{\partial z }\right ) \right |}_{z =1}}=0, \!\! \end{array}\right \} \end{equation}
where
$C_{-2}=C_{-1}=0$
, and
$\mathcal{C}_n^0 (z)= \int _{-\infty }^{\infty } \xi ^n \mathcal{C}^0\, \mathrm{d} \xi$
is the initial vertical distribution of the moment of concentration. The eigenvalue problem is
with
$\eta$
and
$f$
denoting the eigenvalue and eigenfunction, respectively. The boundary conditions are
Note that the above conditions are automatically satisfied because the eddy diffusivity is zero at the boundaries; cf. (2.5). Hence this is a singular Sturm–Liouville problem, and the problem can be transformed equivalently into Legendre’s equation by a simple transformation
$\zeta =2z-1$
, with corresponding boundary conditions given as finite conditions (Barton Reference Barton1983b
). The eigenfunctions can be obtained with the Legendre polynomial
$P_n(\zeta )$
as
and corresponding eigenvalues are
With the discrete set of eigenvalues and eigenfunctions that are normalised and orthogonal, the solution for
$C_n$
from instantaneous initial releases reads
\begin{eqnarray} C_n = \sum \limits _{i=0}^{\infty } p_{ni}(t) \exp {(-\eta _i t)}\,f_i(z),\quad n=0,1,2,\ldots , \end{eqnarray}
where the coefficients
$p_{ni}$
are determined by inner products of initial distributions and eigenfunctions. The definitions of average moments are given by
Specifically,
$M_n$
is the solution of the problem
noting that
$C_{-1}=C_{-2}=0$
, and initial conditions read
The analytical expressions for both local and average moments are detailed in Appendix A.
3. Streamwise dispersion model across all time regimes
3.1. Justification for diffusive description
Taylor’s dispersion model provides an accurate description of the mean concentration in the asymptotic long-time limit. However, the characterisation of the local concentration distribution has traditionally relied on diffusive approximations (cf. Gill Reference Guan and Chen1967; Chatwin Reference Chatwin1970; Smith Reference Smith1982b ), which, despite their practical utility, lack rigorous theoretical justification in the transient regime. In this work, we emphasise that the streamwise dispersion model, formulated directly from the convection–diffusion equation without invoking early averaging or diffusive assumptions, provides a comprehensive and self-consistent solution that remains valid across all time scales. We begin by clarifying the fundamental distinction between local and average moments, which underpins the statistical complexity of transient dispersion processes. Subsequently, we analyse the asymptotic behaviour of phenomenological dispersion coefficients derived from both local and average perspectives, thereby justifying the emergence of diffusive characteristics in Taylor dispersion from a more general streamwise perspective.
Specifically, the first-order average moment
$M_1$
is given by
\begin{eqnarray} M_1= \textit{Pe} t + \textit{Pe} \sum \limits _{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i}\,\overline {u f_i}\frac {1-\exp {(-\eta _i t)}}{\eta _i}. \end{eqnarray}
Here, the overline denotes the cross-sectional average. The leading term
$\textit{Pe} t$
reflects Taylor’s classical result that the centre of mass ultimately propagates at the discharge velocity, whereas the remaining terms represent a small, transient displacement relative to the initial centroid.
The mean centroid position is defined as
$\bar {\nu }_1= {M_1}/{M_0}$
, whereas the local centroid position, dependent on transverse distributions, is given as
$\gamma _1={C_1}/{C_0}.$
Accordingly, the mean drift velocity
$\bar {U}_d$
is defined as the temporal rate of change of the mean centroid position,
\begin{eqnarray} \bar {U}_d = \frac {\mathrm{d}\bar {\nu }_1}{\mathrm{d} t} = \frac {1}{M_0} \frac {\mathrm{d}M_1}{\mathrm{d} t} - \frac {\bar {\nu }_1}{M_0}\frac {\mathrm{d}M_0}{\mathrm{d} t} =\frac {\mathrm{d}M_1}{\mathrm{d} t} =\textit{Pe}+ \textit{Pe} \sum \limits _{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i}\,\overline {u f_i}\exp {(-\eta _i t)}, \end{eqnarray}
while the local drift velocity is expressed as
For asymptotically long times, we have
Hence the transient difference between local and average centroid position is
\begin{eqnarray} \lim _{t \to \infty } \left (\gamma _1-\bar {\nu }_1\right )= \textit{Pe}\sum \limits _{j=1}^{\infty } \frac {{{f}_{\!j}}}{{\eta }_{\!j}} \,\overline {u{{f}_{\!j}}}, \end{eqnarray}
which is independent of time and of the initial conditions. This implies that in the asymptotic limit, the mean drift velocity equals the asymptotic local drift velocity, both approaching the discharge velocity:
Note that differences among these three quantities exist for earlier periods.
Explicit expressions for the eigenfunctions and eigenvalues used in these calculations are listed in table 1. For the line source (i.e.
$\mathcal{C}^0=\delta (\xi )$
and
$\mathcal{C}_0^0=\mathcal{C}_1^0=0$
), with the understanding that
$M_0=C_0=1$
and
$M_1=\textit{Pe}t$
, the first-order local moment
$C_1$
is given by
Explicit expressions of normalised eigenfunctions
$f_i(z)$
and eigenvalues
$\eta _i$
(
$i=1,2,\ldots ,6$
) for streamwise dispersion in a turbulent open channel flow
$0 \leqslant z \leqslant 1$
.

\begin{align} C_1 &=\textit{Pe}t+ \textit{Pe}\sum \limits _{j=1}^{\infty }{{{f}_{\!j}}}\, \overline {u{{f}_{\!j}}}\dfrac { 1-\exp ( -{{\eta }_{\!j}}t )}{{\eta }_{\!j}}\nonumber \\ &=\textit{Pe}t-\frac {1}{8} \left [1-\exp {(-12t)}\right ](2z-1) -\frac {5}{216}\left [1-\exp {(-36t)}\right ](1-6z+6z^2) +\cdots . \end{align}
Thus the difference between local and mean drift velocities is
\begin{eqnarray} U_d^{\star }-\bar {U}_d= \textit{Pe}\sum \limits _{j=1}^{\infty }{{{f}_{\!j}}}\, \overline {u{{f}_{\!j}}}\exp {(-\eta _j t)}, \end{eqnarray}
which decays exponentially with time. Consequently, the local drift velocity is always greater than the average drift, while both tend towards the discharge velocity in the long-time limit. Consistent with Guan & Chen (Reference Guan, Jiang, Tao, Chen and Lee2024), this local velocity is referred to as the ‘streamwise drift velocity’ because this parameter precisely depicts the drift along each streamline, in contrast to the bulk average quantity defined purposely for asymptotic descriptions. We emphasise that only the cross-sectional average of the streamwise drift accurately represents the actual transport behaviour of the solute cloud, whereas its average value coincides with the mean drift only in the asymptotic limit.
Once again, with the initial conditions
$\mathcal{C}_0^0=\mathcal{C}_1^0=\mathcal{C}_2^0=0$
for the line source, the mean variance
$\bar {\sigma }_x^2=M_2/M_0-M_1^2/M_0^2$
reduces to
\begin{eqnarray} \bar {\sigma }_x^2 = 2t+ 2t\textit{Pe}^2+\textit{Pe}^2 t^2 \sum \limits _{i=1}^{\infty }\frac {\overline {u f_i f_i}}{\eta _i} -2\, \textit{Pe}^2 \sum \limits _{i=1}^{\infty }\overline {u f_i f_i} \,\frac {1-\exp {(-\eta _i t)}}{\eta _i^2}. \end{eqnarray}
Note that this variance differs from the local variance, prompting an investigation into the precise nature of this difference. The difference
$\varDelta$
between the average local variance
$\int _0^1 {\sigma _x^{\star }}^2\,\mathrm{d}z = \int _0^1 (C_2/C_0-C_1^2/C_0^2 )\,\mathrm{d}z \equiv \overline {{\sigma _x^{\star }}^2}$
and the mean variance
$\bar {\sigma }_x^2$
is given by
\begin{eqnarray} \varDelta &=& \overline {{\sigma _x^{\star }}^2}- \bar {\sigma }_x^2 =\overline {\left (\frac {C_2}{C_0}- \frac {C_1^2}{C_0^2}\right )} - \big (M_2-M_1^2\big ) \nonumber \\ &=& \overline { C_1^2}- M_1^2 = \textit{Pe}^2 \sum \limits _{i=1}^{\infty } (\overline {u{{f}_{i}}} )^2 \left [\frac {1-\exp \left ( -{{\eta }_{i}}t \right )}{{\eta }_{i}}\right ]^2 \!, \end{eqnarray}
resulting from the order in which vertical averaging and streamwise integral are performed. Equation (3.10) is derived based on the normalisation of eigenfunctions and the known analytical forms of the moments under the line source condition. Precisely,
$\overline {{\sigma _x^{\star }}^2}$
quantifies the average variance over the vertical direction, thereby indicating the extent of dispersion along each streamline, while the mean variance
$\bar {\sigma }_x^2$
corresponds to the variance that one would obtain under the assumption of complete vertical mixing. As time tends to infinity, the discrepancy converges to
\begin{eqnarray} \lim _{t \to \infty } \varDelta = \lim _{t \to \infty } \big (\overline { C_1^2}- M_1^2 \big ) = \textit{Pe}^2 \sum \limits _{i=1}^{\infty }\, \frac {(\overline {u{{f}_{i}}})^2}{\eta _i^2} - \textit{Pe}^2, \end{eqnarray}
which is constant. Note that
$M_0=1$
for this instantaneous pulse release at long times. Further,
$\varDelta \to 0$
as
$t \to \infty$
in this moving coordinate at the speed of mean flow velocity. In other words,
$\bar {\sigma }_x^2$
is only accurate for asymptotically long times, when the drift velocity has reached its uniform value and the solute is vertically well mixed. Yet for short-time dynamics, accurately capturing local drift and dispersivity requires resolving the detailed local structure of the concentration field.
Following the pioneering work of Taylor (Reference Taylor1954), we recall that the longitudinal coordinate is replaced by
$x=\xi -\bar {u} t$
, and streamwise velocity by
$u^\prime =u-\bar {u}$
, where
$\bar {u}$
denotes the dimensionless mean flow velocity. The Taylor–Aris dispersion model is expressed as
possessing a well-established Gaussian solution:
In the long-time limit,
$\bar {D}_T(\infty )$
becomes Taylor’s dispersivity as constant. By multiplying both sides of (3.12) by
$x^2$
, integrating over
$x\in (-\infty ,\infty )$
and applying integration by parts, we obtain the mean dispersivity as
which precisely recovers Taylor’s result in the long-time limit. In parallel with the local variance, a local dispersivity is defined by
\begin{eqnarray} D_T^{\star }(z,t)= \frac {1}{2} \frac {\partial {{\sigma _x^{\star }}^2}}{\partial t} = \frac {1}{2} \frac {\partial }{\partial t}\left [\frac {C_2}{C_0}-\frac {C_1^2}{C_0^2}\right ]\!, \end{eqnarray}
and the average over the cross-section gives rise to the average local dispersivity:
Equation (3.15) is consistent with the definition of streamwise dispersivity used by Vilquin et al. (Reference Vilquin, Bertin, Soulard, Guyard, Raphaël, Restagno, Salez and McGraw2021).
By evaluating the local variance and dispersivity, we show that solute particles do not uniformly sample vertical positions in open channel flows. Moreover, we demonstrate that the average Taylor–Aris dispersivity is a conceptually asymptotic quantity, valid only as a long-time limit of the full solute cloud dynamics. We stress that solely the local dispersivity precisely captures the axial displacement along each streamline and distinctly showcases the notable enhancement of axial spreading. Nevertheless, both dispersivity definitions converge to the same constant in the long-time limit.
Having established the distinction between local and bulk average statistics, it is clear that local moments, rather than their averaged counterparts, are the appropriate quantities for constructing diffusive series expansions of the transient concentration distribution. We now provide further justification for the diffusion-type model, which, extensively employed in practice as an empirical model, lacks solid theoretical foundation in the pre-asymptotic regime.
Following the approach of Guan & Chen (Reference Guan, Jiang, Tao, Chen and Lee2024) in a cylindrical coordinate system, we introduce a convected coordinate system that moves with the local fluid velocity along each streamline, which is devised for the present configuration,
as a convection transformation to decouple convection from diffusion, to give a purely diffusion equation
Using the chain rule, the equivalent diffusivity tensor is expressed as
where
$K(z)$
is exactly the diffusivity introduced in (2.5).
This transformation naturally segregates the diffusivity tensor
$\unicode{x1D63F}$
into three components, each scaling with a different power of the product of the Péclet number and the dimensionless time:
where
The first tensor
$\unicode{x1D63F}^{(\unicode{x1D64A})}$
represents the isotropic turbulent diffusion of soluble matter; the second tensor
${\unicode{x1D63F}^{(\unicode{x1D63E})}}$
denotes a pair of symmetric cross-diffusivities due to the velocity shear; and the third tensor
$\unicode{x1D63F}^{(\unicode{x1D640})}$
quantifies a streamwise diffusion enhancement. With help of (3.21), the purely diffusion equation can be decomposed as
For a given Péclet number, for a short time we obtain a conventional isotropic diffusion equation
and at asymptotically long times, we retain a one-dimensional streamwise diffusion equation with a substitution of the log-law velocity profile as
\begin{equation} \frac {\partial {{C }}}{\partial {{t}}}= K(z)\!\left (1+\frac {\textit{Pe}^2 t^2}{z^2}\right )\,\frac {\partial ^2 {{C }}}{\partial {{x}^{\prime 2 }}}, \end{equation}
parallel to the one-dimensional dispersion equation for mean concentration in Taylor’s theory. This coordinate transformation confirms that the dispersion process is fundamentally diffusive in nature when viewed through the lens of this space- and time-dependent effective diffusivity characterised by (3.19). Crucially, it shows that the enhanced spreading characteristic of Taylor dispersion is not a separate mechanism but emerges naturally from the
$\unicode{x1D63F}^{(\unicode{x1D640})}$
tensor, whose influence grows quadratically with
$\textit{Pe} t$
. This perspective not only justifies the use of diffusive models across all time scales, but also provides a pathway for constructing unified models that bridge the gap between the short-time and asymptotic regimes.
3.2. Derivation of concentration distribution in the moment space
Grounded in first principles of convection–diffusion dynamics, a streamwise dispersion model is formulated for turbulent open channel flows using local moments rather than bulk average statistics. This approach enables a rigorous derivation of the local concentration field via series expansions, capturing non-Gaussian features of the solute distribution. In probability theory, cumulants provide an alternative characterisation to moments; the two sets are equivalent in that they uniquely determine each other. Using this equivalence, the local concentration is analytically expressed in terms of local cumulants, with solutions obtained at various truncation levels.
We define the local probability density function
$P$
of the longitudinal concentration distribution as
which gives the probability of finding a tracer particle at point (
$\xi ,z$
) at time
$t$
. The Fourier transform of
$P$
yields the characteristic function with regard to the angular frequency
$k$
(Kendall & Stuart Reference Kumar, Thomson, Powers and Harris1958; Chatwin Reference Chatwin1970; Jiang & Chen Reference Jiang and Chen2018; Guan & Chen Reference Guan, Jiang, Tao, Chen and Lee2024):
\begin{eqnarray} \varphi (k,z,t) \equiv \int _{-\infty }^{\infty } P \exp (\mathrm{i} k \xi )\,\mathrm{d}\xi =\sum \limits _{n=0}^{\infty }\frac {\left (\mathrm{i}k\right )^n}{n!} \gamma _n, \end{eqnarray}
where
$\gamma _n$
is the
$n$
th-order local raw moment of
$P$
, defined as
Correspondingly, the local central moment of order
$n$
is
The cumulant-generating function is the natural logarithm of the characteristic function, and the cumulants
$\kappa _n$
are defined by the expansion
\begin{eqnarray} \ln \varphi (k,z,t)=\sum \limits _{n=1}^{\infty }{\kappa _n}\frac {\left (\mathrm{i}k\right )^n}{n!}. \end{eqnarray}
Substituting (3.29) into the inverse Fourier transform of
$\varphi$
gives
\begin{equation} \frac {C(\xi ,z,t)}{\int _{-\infty }^{\infty } C(\xi ,z,t)\,\mathrm{d}\xi } =\frac {1}{2\pi }\int _{-\infty }^{\infty } \exp \left [{\sum \limits _{n=1}^{\infty }{\kappa _n}\frac {\left (\mathrm{i}k\right )^n}{n!}}\right ] \exp (-\mathrm{i} k \xi )\,\mathrm{d} k. \end{equation}
Using the identity
together with a Taylor expansion of the exponential involving higher-order cumulants in (3.30), we obtain the series representation
\begin{equation} C(\xi ,z,t)=\frac {{C}_{0}}{\sqrt {2 \pi {{\kappa }_{2}}}}\exp\! \left [ -\frac {{{ (\xi - \kappa _1) }^{2}}}{{2! \, {\kappa }_{2}}}\right ] \left [1+ \frac {\kappa _3}{3!\,\left (\kappa _2\right )^{3/2}} \mathit{He}_{3}\! \left ( \frac {{{ \xi - \kappa _1}}}{{{\kappa }_{2}^{1/2}}} \right ) + \frac {\kappa _4}{4!\,\kappa _2^2} \mathit{He}_{4}\! \left ( \frac {{{ \xi - \kappa _1 }}}{{{\kappa }_{2}^{1/2}}} \right ) +\cdots \right ]\!, \end{equation}
where
$\mathit{He}_{n}$
denotes the Chebyshev–Hermite polynomial of order
$n$
. The cumulants are related to raw moments and central moments by
Note that cumulants coincide with raw moments only for the first order, and with central moments only up to third order; for higher orders, they differ. For ease of interpretation, we introduce phenomenological dispersion coefficients
$\lambda _n$
:
Physically,
$\lambda _1$
is the local mean,
$\lambda _2$
is the local variance,
$\lambda _3$
is the local skewness (quantifying asymmetry), and
$\lambda _4$
is the local kurtosis (indicating peak sharpness). A normalised streamwise coordinate is defined as
so that the probability distribution function in terms of
$X$
has zero mean and unit variance. This coordinate naturally follows the local velocity at short times and the mean flow speed at long times, as discussed in the context of the two time limits (see e.g. (3.23) and (3.24)). In terms of
$X$
, the series solution (3.32) becomes
The truncation order of the streamwise model is set by the available phenomenological dispersion coefficients
$\lambda _n$
. A second-order truncation (retaining only
$\lambda _1$
and
$\lambda _2$
) exactly represents the streamwise drift and dispersivity, while a fourth-order model (including
$\lambda _3$
and
$\lambda _4$
) captures skewness and kurtosis with full accuracy up to that order.
This approach is reminiscent of the method used by Aris (Reference Aris1958) to derive the Gram–Charlier series of type A, later refined by Chatwin (Reference Chatwin1970) through Edgeworth’s modification. Our results are distinguished by the explicit incorporation of local moments and cumulants. The phenomenological dispersion coefficients are time-dependent and locally defined. Consistent with Taylor (Reference Taylor1954), we employ a moving coordinate for visualisation, namely
$x=\xi -\bar {u} t$
, corresponding to a reference frame travelling at the mean flow velocity
$\bar {u}$
.
4. Results and discussion
We first present the local concentration distributions across different regimes, as shown in figure 2. The evolution proceeds through three qualitatively distinct regimes: it begins as a uniform line source, transitions into a logarithmic profile under vertical shear, and eventually develops into a streamwise Gaussian distribution that gradually approaches vertical uniformity. In the initial regime, vertical diffusion is suppressed due to the solute release from a uniform line source. The solute cloud is rapidly reshaped by log-law turbulence, acquiring a logarithmic profile and exhibiting marked asymmetries. This anisotropic distortion results from spatial variations in eddy diffusivity, which enhance streamwise spreading along streamlines. Before Taylor dispersion becomes dominant, solute tends to accumulate near the free surface, where vertical mixing is weaker, leading to an upward concentration bias. The inherent decrease in eddy diffusivity with depth gives rise to an island-shaped local concentration distribution, and contributes to a long-tailed structure in the mean profile.
Transient dispersion regimes for
$\textit{Pe} = 100$
. Local concentration and mean concentration are computed with Monte Carlo simulations: (a,c)
$t= 1.0\times 10^{-4}$
, (b,d)
$t = 0.01$
, (e,g)
$t = 0.05$
, ( f,h)
$t = 5$
.

Interestingly, the mean concentration evolves slowly during the pre-asymptotic phase, despite substantial variation in local turbulent dynamics. This indicates that streamwise dispersion statistics cannot be fully captured by bulk averages alone. This limitation explains why classical drift–diffusion models often fail to represent transient dynamics in the pre-asymptotic regime. Although the spatio-temporal statistics eventually converge to their coarse-grained, asymptotic limits, such averaged descriptions overlook essential features of pre-asymptotic dispersion. At later times, under the combined effects of turbulent convection and eddy diffusion, the concentration field approaches a state of streamwise Gaussianity and vertical uniformity. The strong mixing inherent in turbulent open channel flows shortens the time required for this transition.
The temporal evolution of local variance highlights persistent non-uniformity near the bottom boundary, driven by differences between the local streamwise velocity and the mean flow velocity (figure 3). This non-uniformity is characterised by
$\varDelta$
in (3.10) as a function of the central displacement
$C_1$
and mean displacement
$M_1$
. Initially, dispersion originates near the bottom wall where the shear flow is strongest, and is gradually transmitted upwards. Near the bottom boundaries, the centre of mass moves upstream relative to the bulk flow, whereas near the centreline, it shifts downstream and gradually decelerates as solute from slower-moving layers diffuses across streamlines. This results in a non-monotonic evolution of local dispersivity near the bottom wall, with a slight decrease followed by an overshoot in the intermediate regime, as shown in figure 3(b) from
$t=0.4$
to
$t=0.6$
.
Variation of local variance and dispersivity with
$t$
and
$z$
for
$\textit{Pe}=100$
. (a) Evolution of the vertical profiles of
$\sigma _x^{\star 2}$
from
$t=0.1$
to
$t=1.0$
; (b) vertical profiles of
$D_T^{\star }$
at different times. An overshoot is observed near the channel wall during the intermediate regimes.

The overshoot arises from differences in the relaxation times of the first and second moments. Physically, it reflects how solute trajectories evolve as they interact with the flow field. A tracer released away from the bottom wall diffuses downwards while being advected more rapidly than near-wall fluid, leading to enhanced streamwise spreading relative to purely molecular diffusion. This mechanism explains the early monotonic rise in dispersivity.
As vertical diffusion continues to transport the solute towards the free surface, boundary effects introduce a transient asymmetry in the concentration distribution. This produces the asymmetric overshoot, indicating a nonlinear contribution of Taylor dispersion relative to eddy diffusivity. The effect becomes more pronounced as eddy diffusion weakens. In essence, the overshoot reflects a transient vertical asymmetry that biases the drift velocity and the dispersivity.
At asymptotically long times, the local dispersivity becomes vertically uniform and converges to the mean dispersivity
$\bar {D}_T(\infty )$
, such that the ratio approaches unity (figure 4). In the intermediate regime, however, the spreading rate is higher near the bottom wall than near the free surface, consistent with the temporal evolution of local variance. The initial increase in local dispersivity stems from strong shear dispersion near the bottom, followed by a decline due to the interactions between accelerating and decelerating layers. This leads to a non-monotonic variation of
$D_T^\star$
at
$z=0$
, and a distinct peak in local dispersivity that exceeds the asymptotic value, particularly near the bottom wall, as indicated by the red line in figure 4(b). This peak corresponds to the overshoot in local dispersivity, first reported by Vedel, Hovad & Bruus (Reference Vedel, Hovad and Bruus2014) for steady and unsteady laminar flows from an initial point source – an effect absent for a uniform line source (Vedel & Bruus Reference Vedel and Bruus2012). Here, we demonstrate that such an overshoot can also emerge from a line source in turbulent open channel flows.
Comparing local and mean dispersivity, as shown in figure 4(c), reveals that while both converge to the same asymptotic values, the coarse-grained averaging can substantially overestimate dispersivity, especially at early times. Consequently, the traditional dispersion model may underestimate the degree of non-uniformity in both dispersivity and concentration, leading to inaccuracies in early-time predictions.
Variation of local dispersivity with
$t$
and
$z$
for
$\textit{Pe}=100$
: (a) vertical profiles of normalised local dispersivity from
$t=0.05$
to
$t=1$
; (b) temporal evolution of normalised local dispersivity at different vertical positions; (c) comparisons of local and mean dispersivity.

Variation rate of streamwise concentration between maximum and mean values obtained by the second-order streamwise dispersion model for
$\textit{Pe}=100$
.

To quantify the degree of cross-sectional non-uniformity, we introduce a normalised variation of streamwise concentration as
$V_a(x,t)= [{C(x,z_{m},t)-\bar {C}(x,t)} ]/{M_0}$
, where
$z_m$
is the vertical coordinate at which the concentration reaches its maximum for given
$x$
and
$t$
. Analysis using the second-order model, with precise inputs of local drift and dispersivity, captures the concentration non-uniformity along each streamline (figure 5). In the pre-asymptotic regime, solute spreads downstream significantly faster than the mean flow, resulting in the long-tailed distribution observed in figure 8(a) below. The highest variation rate occurs in the downstream region, reaching up to
$80\,\%$
at
$t=0.01$
in figure 5(a), and exhibits marked asymmetry about the moving frame
$x=0$
. At later times, however, this trend reverses: eddy diffusivity peaks along the centreline, causing the variation rate to drop below
$10\,\%$
for
$t\gt 10$
, and the asymmetry about the centreline gradually diminishes; see figure 5(b). Corresponding to this vertical uniformity, the concentration field becomes perfectly Gaussian in the streamwise direction, as illustrated in figure 8(d) below.
Concentration distributions at
$t=0.01$
obtained by the second-order streamwise dispersion model for
$\textit{Pe}=100$
.

A closer examination of the long tails at
$t=0.01$
(figure 6) reveals that as the flow moves downstream near the surface and upstream near the bottom, the peak concentration values increase and shift upwards. The strong backward flow near the bottom advects the solute cloud upstream (in Taylor’s frame), preventing particles from remaining close to the wall where eddy diffusion is weakest. The monotonic increase in streamwise concentration as layers approach the free surface gives rise to the long-tailed concentration distribution shown in figure 6(b). As also reflected in (3.22), this confirms that the dominant transport mechanism across all time regimes is dispersion along individual streamlines, rather than the asymptotic coarse-grained behaviour by Taylor’s classical theory. Consequently, relying solely on bulk averages of moments or concentration may yield an incomplete – and potentially misleading – understanding of the multi-scale dispersion process.
Average concentration and non-uniformity obtained from the fourth-order streamwise dispersion model for
$\textit{Pe}=100$
in the intermediate regime.

Mean concentration distributions for short and long times obtained from the second-order streamwise dispersion model and Monte Carlo simulations for
$\textit{Pe}=100$
.

To investigate the intermediate regime, we use the fourth-order streamwise dispersion model with locally precise skewness and kurtosis. The mean concentration transitions from a skewed distribution to a Gaussian form (figure 7
a), although significant vertical non-uniformity persists, marked by acceleration near the wall and deceleration near the surface. Consistent with the evolution of local concentration shown in figure 2, the mean concentration also passes through three regimes: the initial, intermediate and Taylor dispersion regimes. The second-order streamwise dispersion model is employed to predict the mean concentration distribution, showing good agreement with Monte Carlo simulations (see figure 8). Numerical details are provided in Appendix B. In the intermediate regime, higher-order inputs such as skewness and kurtosis are required to depict streamwise asymmetries and peaks of concentration distributions accurately. As shown in figure 9, the fourth-order dispersion model gives a satisfactory description of this regime. The curves in figures 8 and 9 are strongly reminiscent of boundary-modulated dispersion reported by Aminian et al. (Reference Aminian, Bernardi, Camassa, Harris and McLaughlin2016). Despite differences in Reynolds numbers, channel boundaries exert a strong influence on dispersion (Aminian et al. Reference Aminian, Bernardi, Camassa, Harris and McLaughlin2016; Vilquin et al. Reference Vilquin, Bertin, Soulard, Guyard, Raphaël, Restagno, Salez and McGraw2021; Zhan, Jiang & Wu Reference Zhan, Jiang and Wu2024), whether through Brownian diffusion at low
$Re$
or turbulent eddy diffusion at high
$Re$
. Considerations of channel aspect ratio are also relevant, as they can produce long-tailed distributions with possible asymmetries.
Mean concentration distributions in the intermediate regimes obtained from the fourth-order streamwise dispersion model and Monte Carlo simulations for
$\textit{Pe}=100$
.

Concentration contours obtained from the fourth-order streamwise dispersion model and numerical simulations using a finite difference method for
$\textit{Pe}=100$
at
$t=0.3, 0.5, 0.9, 1$
.

Figure 10 demonstrates that the fourth-order model effectively captures the two-dimensional structure of concentration, corroborated by numerical simulations. Here, the finite difference method is used to solve (2.6) directly, with corresponding initial and boundary conditions (2.7)–(2.10). The island-like structure, phase delay and concentration peaks in both local and mean concentration distributions across distinct regimes are quantitatively reproduced, showing excellent agreement with numerical results.
At early times, the solute exhibits strong vertical variation. Near the bottom wall, higher shear stretches and disperses the solute efficiently, whereas the reduced shear near the free surface slows this process, allowing the local concentration to remain elevated, as shown in figure 6(c). A compact island-shaped region of high concentration then forms near the surface. This structure reflects the initial stretching of the concentration profile by the velocity field. Fast convection along the surface, combined with weak vertical mixing, sustains this feature. Over time, eddy diffusion transports solute downwards while longitudinal convection carries it downstream, causing the island-shaped patch to dissipate.
These results can be placed within the broader context of dispersion modelling across distinct flow regimes. At low Reynolds numbers, as shown by Vedel & Bruus (Reference Vedel and Bruus2012) and Vedel et al. (Reference Vedel, Hovad and Bruus2014), transient dispersion in viscous-dominated time-dependent flows arises from molecular diffusion modulated by shear. Analytical solutions for moments have been extended to specific oscillatory flows (Ding et al. Reference Elder2021; Guan et al. Reference Guo, Jiang and Chen2021; Jiang & Chen Reference Jiang, Zeng, Fu and Wu2026; Wang et al. Reference Wang, Jiang, Zeng, Wu and Wang2025b ) By contrast, classical studies by Taylor (Reference Taylor1954) and Elder (Reference Fischer1959) demonstrated that in turbulent flows at high Reynolds numbers, dispersion is primarily driven by eddy-induced exchange across velocity gradients. Although both regimes are well described by convection–diffusion equations, the underlying physical mechanisms differ fundamentally.
A key distinction lies in the representation of streamwise diffusivity. In laminar regimes, the baseline process is isotropic Brownian diffusion, which is unaffected by shear. Local dispersivity is then rigorously defined and commonly employed (Vilquin et al. Reference Vilquin, Bertin, Soulard, Guyard, Raphaël, Restagno, Salez and McGraw2021; Guan & Chen Reference Guan, Jiang, Tao, Chen and Lee2024). In turbulent systems, however, diffusivity varies with depth due to the anisotropy of eddy mixing, and this vertical structure governs the effective local dispersivity. The convection–diffusion equation therefore requires a depth-dependent turbulent diffusivity, placing the analysis firmly in the turbulent dispersion literature.
From this perspective, Taylor’s classical theory emerges as a limiting case within the general streamwise dispersion framework. This generalised approach can be viewed as an effective field theory, in which local statistics converge to asymptotic coarse-grained limits without the need for pre-averaging. Taylor’s bulk-averaged values then naturally appear as limiting cases rather than imposed assumptions. The framework also extends to more complex cases, such as secondary flows in two or three dimensions (Stone & Brenner Reference Stone and Brenner1999), micro-scale particle–boundary interactions, and reactive dispersion where transport is non-conservative (Shapiro & Brenner Reference Shapiro and Brenner1986).
Connecting the laminar and turbulent perspectives highlights the importance of modelling choices. Laminar approaches rest on molecular diffusion enhanced by shear, while turbulent models replace it with an effective eddy diffusivity. This explains why a constant diffusivity fails to capture turbulent mixing, while a depth-dependent turbulent diffusivity reduces to a constant in the laminar limit.
In summary, these comparisons clarify unique features of turbulent dispersion and demonstrate the generality of a unified streamwise framework for shear-enhanced transport. Although tailored to turbulent open channel flows, this streamwise perspective naturally connects with laminar dispersion (also see Guan & Chen Reference Guan, Jiang, Tao, Chen and Lee2024), offering a consistent physical foundation for modelling concentration fields across the spatio-temporal regimes and the Reynolds number spectrum.
5. Conclusions
Taylor dispersion in turbulent open channel flows plays a critical role in engineering and environmental applications, including streams, estuaries and large-scale water bodies. Yet existing predictive models rely heavily on bulk average statistics, which obscure the underlying local physical mechanisms. Addressing dispersion across all time regimes requires identifying the dominant processes while retaining both local statistics measures and their spatial averages. Here, we develop a streamwise framework that characterises concentration, drift, dispersivity, skewness and kurtosis distributions as local spatio-temporal quantities. Using a Lagrangian coordinate system, we generalise Taylor’s classical theory to describe turbulent dispersion in open channels, preserving the central role of diffusive transport along each streamline.
Taylor’s dispersion theory is asymptotically valid only after tracers have fully sampled the channel cross-section. Nevertheless, concentration moments offer a unified means of capturing dynamics across the Reynolds number spectrum and across all time regimes. We show that the local drift term converges to the bulk velocity at long times, although turbulent fluctuations prevent a prefect match with the Eulerian drift velocity. Similarly, local dispersivity cannot be inferred solely from the mean variance, highlighting the limitations of conventional drift–diffusion models in the pre-asymptotic regime. From a streamwise perspective, we derive an analytical solution that characterises the essential spatio-temporal features. In turbulent shear flows, dispersivity consistently exceeds the eddy diffusivity, scales inversely with it in the long-time limit, and is strongly modulated by velocity variations along streamlines.
The proposed model captures the essential physics of local cumulants while remaining analytically tractable, especially in regimes where traditional coarse-grained averaging proves inadequate. In pre-asymptotic regimes, displacement and variance evolve differently near the wall and near the centreline, with symmetry breaking inducing an overshoot in dispersivity before convergence to the asymptotic Taylor–Aris values. By incorporating precise local drift and dispersivity along each streamline, the second-order model suffices for short and long times, while the fourth-order model performs well at intermediate times. Theoretical predictions show strong agreement with numerical simulations.
Whereas prior work has largely focused on asymptotic regimes, our results highlight the persistence of spatial-temporal variability and importance of dynamic local structures. These features can substantially enhance mixing and dispersion, with important implications for the transport of both passive and active matter. Our comprehensive solution yields testable predictions for large-scale transport and mixing in turbulent channel flows.
Overall, this work interprets Taylor’s framework as a coarse-grained limit of a more general streamwise theory. By embedding local statistics, the model captures spatio-temporal evolution beyond early averaging, and extends dispersion theory to broader classes of transport, including high-Reynolds-number flows, reactive systems and tailored manipulation of active matter (Shapiro & Brenner Reference Shapiro and Brenner1986; Stone & Brenner Reference Stone and Brenner1999; Yan et al. Reference Yan2024; Chen et al. Reference Chen, Jiang, Guo, Zeng and Guan2025). The proposed framework thus offers a unified and extensible foundation for understanding turbulent dispersion and its role in complex transport processes across scales.
Acknowledgements
The authors thank Professor Luoyi Tao for his notes on the convection transformation, and Ling Wen for discussions on numerical computation.
Funding
This work is supported by the National Natural Science Foundation of China (grant nos 123B2039, 12372379 and 52079001). M.Y.G. also acknowledges support from the Fellowship Programme of CPSF (grant no. GZC20251266) and the Young Scientists Fund of Key Laboratory for Mechanics in Fluid Solid Coupling Systems, Chinese Academy of Sciences.
Declaration of interests
The authors report no conflict of interest.
Appendix A. Exact solutions of local and average moments
Using the method of separation of variables, explicit solutions of transient moments can be found recursively (Barton Reference Barton1983b , Reference Barton1984; Guan et al. Reference Guan, Zeng, Li, Guo, Wu and Wang2022; Jiang et al. Reference Kalinske and Pien2022). Explicit transient solutions of the first few local and average moments are given in this appendix for reference.
The zeroth-order average moment is
$M_0=1$
. The explicit solution for the zeroth-order local moment
$C_0$
is found to be
$C_0=1+ \sum_{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i} f_i \exp {(-\eta _i t)}.$
The first-order average moment
$M_1$
reads
$M_1= \textit{Pe} t + \textit{Pe} \sum_{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i}\,\overline {u f_i}({1-\exp {(-\eta _i t)}})/{\eta _i}$
. The first-order local moment
$C_1$
is
\begin{align} C_1 ={}& \textit{Pe} t+\textit{Pe} \sum \limits _{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i}\,\overline {u f_i} \dfrac {1-\exp {(-\eta _i t)}}{\eta _i} +\sum \limits _{j=1}^{\infty }{{{f}_{\!j}}\,\overline {{{\mathcal{C}}_{1}^{0}}{{f}_{\!j}}}}\exp \big ( -{{\eta }_{\!j}}t \big )\nonumber \\ &{}+ \textit{Pe}\sum \limits _{j=1}^{\infty }{{{f}_{\!j}}}\, \overline {u{{f}_{\!j}}}\dfrac { 1-\exp \big ( -{{\eta }_{\!j}}t \big )}{{\eta }_{\!j}} +\textit{Pe} t \sum \limits _{i=1}^{\infty }{\overline {{{\mathcal{C}}_{0}^{0}}{{f}_{i}}} \,\overline {u{{f}_{i}}{{f}_{i}}}}{{f}_{i}}\exp \left ( -{{\eta }_{i}}t \right )\nonumber \\ &{}+\textit{Pe} \mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{j=1}^{\infty }} \limits _{i \neq j} {{\overline {{{\mathcal{C}}_{0}^{0}}{{f}_{i}}}\dfrac {\overline {u{{f}_{i}}{{f}_{\!j}}}}{{{\eta }_{\!j}}-{{\eta }_{i}}}}} {{f}_{\!j}}\left [ \exp \left ( -{{\eta }_{i}}t \right )-\exp \big ( -{{\eta }_{\!j}}t \big ) \right ]\!. \end{align}
The second-order average moment
$M_2$
is
\begin{align} {{M}_{2}} ={}& 2t+\textit{Pe}^2 t^2 + 2\textit{Pe}^2 t \sum \limits _{i=1}^{\infty } \dfrac { \overline {\mathcal{C}_0^0 f_i}\,\overline {u f_i}\,\overline {u f_i}}{\eta _i} +2\textit{Pe}^2 t \sum \limits _{i=1}^{\infty }\dfrac {\overline {u f_i}\,\overline {u f_i}}{\eta _i} \nonumber \\ &{}- 2\, \textit{Pe}^2 \sum \limits _{i=1}^{\infty }\overline {u f_i}\,\overline {u f_i} \,\dfrac {1-\exp {(-\eta _i t)}}{\eta _i^2} +2\sum \limits _{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i}\, \overline {K f_i} \dfrac {1-\exp {(-\eta _i t)}}{\eta _i}\nonumber \\ &{}+2\textit{Pe} \sum \limits _{i=1}^{\infty } \overline {\mathcal{C}_1^0 f_i}\, \overline {u f_i}\dfrac {1-\exp {(-\eta _i t)}}{\eta _i} - 2\textit{Pe}^2 t \sum \limits _{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i}\,\overline {u f_i}\, \overline {u f_i f_i}\,\dfrac {\exp {(-\eta _i t)}}{\eta _i}\nonumber \\ &{}+ 2\textit{Pe}^2 \sum \limits _{i=1}^{\infty } \overline {\mathcal{C}_0^0 f_i}\,\overline {u f_i} \, \overline {(u-1) f_i f_i}\dfrac {1-\exp {(-\eta _i t)}}{\eta _i^2}\nonumber \\ &{}+ 2\textit{Pe}^2 \mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{j=1}^{\infty }} \limits _{i \neq j} \,\dfrac {\overline {u f_i f_{\!j}}}{\eta _{\!j}-\eta _i} \big (\overline {\mathcal{C}_0^0 f_{\!j}}\,\overline {u f_i}+\overline {\mathcal{C}_0^0 f_i}\,\overline {u f_{\!j}}\big ) \dfrac {1-\exp {(-\eta _i t)}}{\eta _i}. \end{align}
The second-order local moment is
\begin{align} \displaystyle C_2={}& \sum \limits _{i=1}^\infty \textit{Pe} t^2\, \overline {\mathcal{C}_0^0 f_i}\, \overline {u f_i f_i} \exp {(-\eta _i t)} + \sum \limits _{i=1}^\infty 2\,\overline {\mathcal{C}_0^0 f_i}\, \overline {f_i f_i}\, t \exp {(-\eta _i t)} \nonumber \\ &{}+\mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{j=1}^{\infty }} \limits _{i \neq j} 2\textit{Pe} t\, \overline {\mathcal{C}_0^0 f_{\!j}}\,\overline {u f_i f_{\!j}}\, \overline {u f_{\!j} f_i} \dfrac {\exp {(-\eta _i t)}}{\eta _{\!j}-\eta _i} +\mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{k=1}^{\infty }} \limits _{k \neq i} 2\textit{Pe} t\, \overline {\mathcal{C}_0^0 f_k}\,\overline {u f_i f_k}\, \overline {u f_i f_i} \dfrac {\exp {(-\eta _i t)}}{\eta _k-\eta _i}\nonumber \\ &{}+\mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{j=1}^{\infty }} \limits _{i \neq j} 2\, \textit{Pe}^2\, \overline {\mathcal{C}_0^0 f_{\!j}}\,\overline {u f_{\!j} f_{\!j}} \,\overline {u f_i f_{\!j}} \dfrac {\exp {(-\eta _i t)}-\exp {(-\eta _{\!j} t)}+(\eta _i-\eta _{\!j})t \exp {(-\eta _{\!j} t)}}{\left (\eta _i-\eta _{\!j}\right )^2}\nonumber \\ &{}+\mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{j=1}^{\infty }} \limits _{i \neq j} 2\, \overline {\mathcal{C}_0^0 f_{\!j}}\, \overline {f_i f_{\!j}} \dfrac {\exp {(-\eta _{\!j} t)}-\exp {(-\eta _i t)}}{\eta _i-\eta _{\!j}} \nonumber \\ &{}+\mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{j=1}^{\infty } \sum \limits _{k=1}^{\infty }} \limits _{k \neq j,\ k\neq i} 2\textit{Pe}^2\, \overline {\mathcal{C}_0^0 f_k}\,\overline {u f_{\!j} f_k}\,\overline {u f_i f_{\!j}} \dfrac {\exp {(-\eta _k t)}-\exp {(-\eta _i t)}}{(\eta _k-\eta _i)(\eta _k-\eta _{\!j})}\nonumber \\ &{}+\mathop {\sum \limits _{i=1}^{\infty } \sum \limits _{j=1}^{\infty } \sum \limits _{k=1}^{\infty }} \limits _{k \neq j,\ j\neq i} 2\textit{Pe}^2\, \overline {\mathcal{C}_0^0 f_k}\,\overline {u f_{\!j} f_k}\,\overline {u f_i f_{\!j}} \dfrac {\exp {(-\eta _{\!j} t)}-\exp {(-\eta _i t)}}{(\eta _k-\eta _{\!j})(\eta _i-\eta _{\!j})}. \end{align}
The
$n$
th-order local moment
$C_n$
may be very tedious and can be computed recursively by the integral
\begin{eqnarray} C_n = \sum \limits _{i=1}^{\infty } \exp {\left (-\mu _i t \right )}\, f_i \left [ \int _0^1 f_i \mathcal{C}_n^0\,\mathrm{d}z + \int _0^t \exp {(\mu _i \tau )}\, \chi (\mu _i, \tau )\, \mathrm{d}\tau \right ]\!. \end{eqnarray}
Appendix B. Monte Carlo simulations
We start with the convection–diffusion equation presented in the main text:
Expanding the vertical diffusion term and rearranging yields an equivalent form that separates an effective convective term from the purely diffusive part:
Assuming that solute particles undergo a random walk, the convection–diffusion equation (B1) is equivalent, in the sense of the Fokker–Planck equation, to the following system of Itô stochastic differential equations (Öttinger Reference Ouyang, Li, Lin, Lin and Yu1996; Chirikjian Reference Chirikjian2009):
Here,
$\mathrm{d} w_x$
and
$\mathrm{d} w_z$
are independent Wiener processes representing eddy diffusion in the longitudinal and vertical directions, respectively. The drift term
$-{\partial K(z)}/{\partial z}$
in the
$z$
-equation arises from the spatial variation of the diffusivity and ensures that the corresponding Fokker–Planck equation reproduces (B2). Appropriate boundary conditions (e.g. reflection at the bed and water surface) must be imposed when simulating a confined channel; in the present work, we employ reflecting boundaries at
$z=0$
and
$z=1$
(see main text for continuum descriptions).
The stochastic differential equations are discretised using the explicit Euler–Maruyama scheme with constant time step
$\mathrm{d}t = 10^{-4}$
. A total of
$N=5\times 10^{5}$
particles are released, and the implementation of this grid-free simulation is inherently parallelised over many CPU cores (Kumar et al. Reference Li2021), through which the computation time can be efficiently compressed.
From the computed trajectories, the concentration field is reconstructed by binning the particle positions into a histogram. The longitudinal moments are then estimated as ensemble averages:
\begin{eqnarray} M_1(t) = \frac {1}{N} \sum \limits _{i=1}^N x_i(t), \end{eqnarray}
\begin{eqnarray} \bar {\sigma }_x^2 = \frac {1}{N} \sum \limits _{i=1}^N \big (x_i^2(t) - M_1^2(t)\big ), \end{eqnarray}
where
$x_i(t)$
denotes the streamwise coordinate of particle
$i$
at time
$t$
. These sample moments correspond to the continuum definitions of the mean displacement and variance used in the main text.






























