Citation: Jejeniwa, O.A.; Gidey,
H.H.; Appadu, A.R. Numerical
Modeling of Pollutant Transport:
Results and Optimal Parameters.
Symmetry 2022, 14, 2616. https://
doi.org/10.3390/sym14122616
Academic Editors: Clemente
Cesarano and Juan Luis García
Guirao
Received: 8 September 2022
Accepted: 30 November 2022
Published: 9 December 2022
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symmetry
S S
Article
Numerical Modeling of Pollutant Transport: Results and
Optimal Parameters
Olaoluwa Ayodeji Jejeniwa
1
, Hagos Hailu Gidey
2
and Appanah Rao Appadu
1,
*
1
Department of Mathematics & Applied Mathematics, Nelson Mandela University,
Gqeberha 6031, South Africa
2
Department of Mathematics and Statistical Sciences, Botswana International University of Science
and Technology, Palapye Private Bag 16, Botswana
* Correspondence: rao.appadu@mandela.ac.za or rao.appadu31@gmail.com
Abstract: In this work, we used three finite difference schemes to solve 1D and 2D convective
diffusion equations. The three methods are the Kowalic–Murty scheme, Lax–Wendroff scheme, and
nonstandard finite difference (NSFD) scheme. We considered a total of four numerical experiments;
in all of these cases, the initial conditions consisted of symmetrical profiles. We looked at cases when
the advection velocity was much greater than the diffusion of the coefficient and cases when the
coefficient of diffusion was much greater than the advection velocity. The dispersion analysis of
the three methods was studied for one of the cases and the optimal value of the time step size k,
minimizing the dispersion error at a given value of the spatial step size. From our findings, we
conclude that Lax–Wendroff is the most efficient scheme for all four cases. We also show that the
optimal value of k computed by minimizing the dispersion error at a given value of a spacial step
size gave the lowest l
2
and l
∞
errors.
Keywords: finite difference schemes; amplification factor; stability; relative phase error; optimization
1. Introduction
Petroleum is used as fuel for daily human activities. Liquid petroleum has some useful
advantages over other energy sources; it is concentrated and could be easily transported
from one point to another.
The major objective of oil spill modeling is to predict where oil is likely to go after
a spill [1,2]. The use of data on ocean currents, winds, waves, and other environmental
factors help in this regard [3]. Ovsienko et al. [4] developed a model to forecast the behavior
and spreading of oil at sea using the particle-in-cell technique on a quasi-Eulerian adaptive
grid. The fate and behavior of spilled oil can be affected by nine physical, chemical,
and biological processes: advection, spreading, evaporation, dissolution, emulsification,
dispersion, auto-oxidation, biodegradation, and sinking/sedimentation [5].
Cho et al. [1] analyzed the movement of oil with a numerical model that solved an
advection–diffusion reaction equation with finite difference schemes. The spilled oil dis-
persion model was established in consideration of tide and tidal currents, simultaneously.
They obtained the velocity components in the advection–diffusion reaction equation from
the shallow water equations. Another commonly used method is the split-operator ap-
proach where the convection and diffusion terms are solved by two different numerical
methods [6]. A one-dimensional convective diffusion equation was solved by Noye–Tan [7]
using the third-order semi-implicit finite difference method. This approach was later ex-
tended by Noye–Tan [8] to solve the two-dimensional convective diffusion equation but the
said method had issues handling three-dimensional problems because of the large matrix
inversion at each time step. The quadratic upstream interpolation convective kinematics
(QUICK) method for one-dimensional unsteady flow was introduced by Leonard [9] to
address the issue of numerical dispersion. This method was extended to an improved
Symmetry 2022, 14, 2616. https://doi.org/10.3390/sym14122616 https://www.mdpi.com/journal/symmetry