1. Introduction
The ocean exhibits motions over an amazing range of scales, from the 1000 km scales of ocean gyres, to sub-centimeter scales on which viscous dissipation removes energy from the system. Modern oceanography relies on field measurements, remote sensing, and increasingly, numerical simulation of ocean processes. All of these have their own established methodology, yet all fail to provide a complete description of the ocean. However, the influence of physical processes on biogeochemical ocean dynamics is an active area of research in which numerical models play an important role as investigative and predictive tools[
1,
2,
3,
4,
5]. The performance of numerical models is limited by the underlying numerical method and the model resolution. This is in turn limited by the availability of computational resources. Ocean modellers must thus make choices as to which processes to resolve, which to parameterize, and at times, even which to ignore.
The Regional Ocean Modelling System (ROMS) is a popular tool for conducting regional (on the order of 10s of kilometres) simulations due to its flexibility and stable numerical methodology. It has a topography-following coordinate system in the vertical, an implicit free-surface, and can be run as a coupled physical-biogeochemical model[
6]. ROMS is a split-explicit model, meaning fast and slow dynamics are split into sub-problems. If non-dissipative time-stepping is used for both, the model becomes unstable[
7,
8]. Time-stepping algorithms with forward-backward feedback are used to enhance the internal stability of the model[
9]. In addition to the numerical diffusivity introduced by the time–stepping method, ROMS treats horizontal and vertical diffusion differently, and has a number of options for parameterizing vertical mixing[
7,
10] all of which are, by nature, dissipative[
11]. While not strictly necessary, the majority of regional modeling studies invoke the hydrostatic approximation, meaning some processes (e.g. density overturns) are inherently excluded from consideration. Example use cases for ROMS include the Atlantic Canada Model (
km) horizontal resolution and 30 vertical levels)[
12], the Coupled-Ocean-Atmosphere-Wave-Sediment-Transport modeling system (4.7-9.0km horizontal resolution, 50 vertical layers spanning 8km)[
13], and studies of storm induced circulation and hydrography changes in tropical regions (6km resolution)[
14]. The diversity of studies that use ROMS indicates the importance of model flexibility and adaptability.
ROMS, and similar models, effectively solve the Reynolds Averaged Navier-Stokes (RANS) equations. Reynolds averaging is a commonly applied procedure in the study of turbulent flows [
15]. It consists of decomposing a physical quantity into its ensemble mean and fluctuating parts. The procedure will be illustrated in
Section 2.1.1. The appeal of RANS simulations comes from the reduced computational cost of simulating only the mean state of a system as opposed to running an ensemble of simulations. However, ensemble averaging the Navier-Stokes momentum equation introduces the Reynolds stress tensor which poses a closure problem[
15]. Despite the challenge of parameterizing the Reynolds stresses, RANS is a popular method for simulating naturally occurring turbulent flows, which are ubiquitous in the oceans and atmosphere and known to cause strong mixing[
16,
17]. Turbulent flows are characterized by large, irregular variations in space and time, making their details unpredictable [
18]. These variations often manifest in the form of vortices or filaments. For a discussion of several classes of models, as well as popular modelling techniques and closures when using RANS for turbulence modelling see [
19]. For a review of the uncertainty in RANS models see [
20].
Eddy viscosity models are the most common choice for parameterizing Reynolds stress terms, largely owing to their relative simplicity. These models assume that the Reynolds stress tensor is aligned with the mean strain tensor allowing the Reynolds stress term to be related to the ensemble mean velocity field[
15,
18]. In practice, the Reynolds stress terms in the RANS momentum equation are replaced by simply introducing additional viscosity into the system[
15]. These models assume that the local gradient of the mean velocity field dictates the direction of flux. However, if the advection in a turbulent flow is strong enough, the large eddies that emerge may dominate and cause the flux to be oriented against the gradient[
18], making the eddy viscosity assumption invalid. In particular, there are cases in which the eddy viscosity becomes negative and the model breaks down because anti-diffusion is mathematically ill-posed[
21].
Analogously, the Reynolds fluxes that emerge from Reynolds averaging scalar transport equations are often modelled by eddy diffusivities. Eddy diffusivities have been estimated for passive tracers with satellite observations and found to be strongly space and time dependent[
22]. In the upper 2000m of the oceans, horizontal eddy diffusivities on a 300km scale range between
m
/s and
m
/s[
23,
24,
25]. The choice of expression used to calculate eddy diffusivity inevitably affects the estimate. If one were to consider the suppression of mixing by mean currents, the spatial distribution and magnitude of the eddy diffusivities changes dramatically[
26] as compared to estimations that simply use mixing length theory[
27]. Evidence has suggested that in stratified fluids, the ocean being a prime example, eddy diffusivity should be modelled as a decreasing function of buoyancy frequency[
28].
Eddy mixing is also strongly dependent on the tracer being considered[
29]. Active tracers may require counter-gradient fluxes as opposed to down gradient fluxes resulting in negative eddy diffusivities[
30]. For instance, double diffusion displays counter-gradient density flux while turbulence transports density upwards[
31]. Though some methods for determining eddy diffusivities and transport characteristics have shown indistinguishable performance when used for passive or active tracers[
32], this cannot be the case for reactive tracers, the dynamics of which are inevitably more complicated.
The effect of turbulence on the reaction dynamics of nutrient phytoplankton zooplankton (NPZ) models has been considered from several different lenses[
33,
34,
35]. NPZ models are almost always expressed in terms of advection-diffusion-reaction (ADR) equations. Complications arise from the impact of turbulence on the spatial distribution of a reactive tracer possibly affecting the reaction rate[
35]. Further, eddy reaction terms, defined as covariances of tracer fluctuations, are introduced when the reaction function is Reynolds averaged. Eddy reactions are inevitably strongly reaction dependent and have been shown to be sensitive to seasonality, location, and spatial scales for some NPZ models[
36].
In addition to being a popular tool for examining oceanic ecosystems, RANS has been used to model reactive tracers in the contexts of water disinfection[
37,
38,
39], the spread of air pollutants[
40], and combustion[
41]. In this paper, we take a step back and consider a simple system in which a reactive tracer grows according to Fisher’s equation within a Rayleigh-Taylor (RT) flow. So called “toy" flows, for which velocities are specified instead of solved for, have proven to be a useful tool for conducting initial investigations into the effect of turbulence on phytoplankton[
34]. Velocities are often chosen so that the flow field is composed of convective cells of multiple scales that oscillate in space [
34,
42]. The cells are intended to represent flows due to thermal convection and the range of scales is introduced to mimic turbulence. They are thought to be especially useful when considering under-ice convection as ice cover eliminates all wind-driven turbulent mixing[
42,
43]. However, this method fails to capture the cascade of energy between scales in turbulent flows nor does it account for the dissipation of turbulent kinetic energy, making it a poor representation of ocean dynamics.
We choose Rayleigh-Taylor instability-induced turbulent mixing as a non-trivial, yet well studied illustrative example. From
Figure 2 in [
44], it is apparent that RT flows are not cell-like and evolve into turbulent states. For a discussion of several turbulence model choices for RT instabilities, see [
45,
46]. RT instabilities have some memory of the spatial structure of their initial conditions when we consider large-scale effects, but the smaller-scale internal structure makes the mixing unpredictable[
47]. Two dimensional simulations fail to capture the internal structure of the flow and thus cannot describe the turbulent mixing that would be seen in three dimensions[
44,
47,
48]. For the purpose of constructing an illustrative example, however, two dimensional simulations will suffice.
The simplicity of the numerical experiment reported herein allows us to illustrate the differences between passive and reactive tracer fields evolving under turbulence. In particular, we illustrate that the evolution of a reactive tracer is poorly captured by the ensemble mean and that eddy diffusivity parameterizations are not appropriate for our simulations. The remainder of this paper is structured as follows. In
Section 2 we present the governing equations and demonstrate how Reynolds averaging can be applied to ADR equations. Results from an ensemble of 50 simulations will be presented in
Section 2.2 to illustrate differences in the effects of turbulent mixing on a passive tracer versus on a reactive tracer growing according to Fisher’s equation. The limitations of using RANS simulations to model reactive tracers will be discussed in
Section 4.
4. Discussion
Turbulent flows are highly unpredictable and disordered. In this study, small perturbations to the shape of the initially unstable density stratification were enough to produce significant variability within an ensemble of 50 well-resolved simulations. RANS simulations implicitly assume that the most important dynamics are captured by the mean. We have shown that this assumption fails when considering the transport of a reactive tracer growing according to Fisher’s equation.
Under Reynolds averaging, the mean reaction equation is altered by the introduction of eddy reaction terms. The procedure in
Section 2.1.2 can be applied to any polynomial reaction function. Even non-polynomial reaction functions could be subjected to the same procedure if they were approximated by Taylor polynomials. The procedure allows one to isolate the roles of the mean, fluctuations, and mean-fluctuation interactions in the Reynolds averaged reaction function. It also tells us that any terms raised to an even power will introduce sources or sinks (depending on the sign of the coefficient) into the mean ADR equation which depend only on the fluctuations. For Fisher’s equation, a sink in the mean ADR equation transfers concentration to the fluctuations. Growth, whether in the mean or fluctuations, increases diffusion allowing a reactive tracer to spread to parts of the domain that a passive tracer may not reach. These areas may include turbulent structures further transferring concentration from the mean to the fluctuations. Diffusion and turbulent mixing push the tracer concentration away from its stable equilibrium,
, thereby promoting further growth and creating a positive feedback loop. Numerical dispersion, while not significant in our pseudospecral simulations, has the potential to artificially increase the diffusivity of a tracer. The positive feedback would thus be intensified in an inherently dissipative model (i.e. one based on finite volumes) such as ROMS[
11].
Due to the flux of concentration from the mean to the fluctuations, the mean underestimates the tracer concentrations in the individual simulations. Further, as shown by the supplementary movies, the downwards propagation of the reactive tracer is captured by the fluctuations and not the mean. In a true RANS simulation, one has no knowledge of the Reynolds stresses, eddy fluxes, or eddy reactions. In our numerical experiment, these quantities have proven to have a significant effect on the downward propagation of the reactive tracer. The bulk scalar variances (which are also the eddy reactions for Fisher’s equation) for both the passive and reactive tracers are approximately 1/4 the magnitude of the corresponding bulk mean and thus certainly non-negligible.
Given the initial distribution of the tracers (panel (b) of
Figure 1), the generation of turbulent mixing with a RT instability doomed eddy diffusivity relations to fail. RT bubbles pushed up against the tracer fronts therefore causing counter-gradient fluxes and negative eddy diffusivities. As the fronts of the RT plumes hit the top and bottom of the domain, the flow transitioned from a state dominated by large scale motions to one dominated by smaller scale turbulent mixing. In the latter state, negative eddy diffusivities continue to be observed because the largest eddies are larger than the curvature of the mean vertical tracer profiles[
18]. Negative eddy diffusivities have been observed in numerical studies of non-passive oceanic tracers and attributed to symmetric instabilities and other submesoscale phenomena[
30] in agreement with the results presented herein. We would expect an eddy diffusivity parameterization to perform equally as bad if not worse for the same setup in three dimensions since the eddy diffusivity parameterization does not account for vortex tilting[
51].
Due to the feedbacks observed between turbulent mixing and the reaction dynamics, we stress the importance of conducting studies of reactive tracers with turbulent flows. The use of convective cells to approximate turbulence is problematic primarily because the cells introduce streamlines that the tracer can only diffuse across[
34,
42]. Turbulent RT-induced mixing created small, irregular structures that pulled the reactive tracer into parts of the domain it otherwise could not have reached. There was a significant amount of variability in the tracer distributions of our ensemble members. With pre-specified velocity fields, it will be near impossible to capture the structures that characterize turbulent mixing and thus variability in the tracer distribution will be underestimated.
In addition to the flow used to induce turbulent mixing, the results of this study are highly specific to the reaction and Damköhler number selected. We chose
to balance the effects of advection with those of the reaction. The balance causes growth and mixing processes to become coupled and eddy diffusivity parameterizations to fail[
55]. Ocean tracer dynamics are complex so interactions between turbulent mixing and reaction dynamics are not as simple as the positive feedback we observed in our study[
35,
50,
56].
When considering a slow reaction with
or smaller, the coupling will be weaker but new challenges arise as turbulent mixing creates sharp tracer filaments. Decreasing
to
made our 0.5mm grid spacing insufficient to resolve the tracer filaments. This is problematic, given the large disparity between the scale of our simulations and any regional modeling study. Increasing the diffusivity of the tracer would smooth out the fronts thereby reducing the demand for a higher resolution. In a RANS simulation, this is done through eddy diffusivity parameterizations. Modeling studies based on ROMS generally have
to
kilometer horizontal resolution and
to
meter vertical resolution[
13,
14,
57]. Therefore, it should be assumed that tracer distributions in these models have been over-smoothed. Further, the spacing between ROMS grid points is not uniform and the vertical resolution is often better near the surface than at the bottom (O(1m) versus O(200m) [
56]). A possible improvement may be simulating near surface effects, which are weighed more heavily due to the grid spacing, while parameterizing those deeper in the domain.
Future directions for this work include running simulations with a deeper domain to allow for a longer transport period before the free slip walls begin to affect the flow. Though two dimensional RT instabilities were sufficient for this study, their mixing characteristics are well-known to differ from their three dimensional counterparts[
44,
47]. It would be interesting to determine whether a three dimensional RT instability affects the reactive tracer any differently, for example through organized larger scale motions. Another possible avenue for exploration may be to use the data from the ensemble generated for this study to force simulations of the mean ADR equation. These simulations would allow the effects of the eddy flux and eddy reactions to be isolated and allow for the evaluation of potential parameterizations.