
of the concentration in one point to the
phenomena of diffusion and transportation
in the atmosphere, the concentration of air
pollutants in the atmosphere is directly
linked to air quality. High ground level air
pollution concentration can affect both the
public’s health and the environment. There
are regulations in many countries that
require the applicant to do an air dispersion
modeling in order to obtain an approval
certificate for building a new facility.
Dispersion models can be used to predict the
cumulative effect of existing and planned
facilities. In order to predict Ground Level
Concentration (GLC) from various sources,
atmospheric dispersion models are essential.
In the setting of the modeling of the
scattering of the pollutants in the atmosphere
it remains to try to solve the equation
diffusion-transportation bound to the
concentrations of pollutants only. To solve
this equation various possibilities offer
themselves based: - on an algebraic
approach, and a numeric approach
In a first time we have, as makes usually
for reasons of calculation capacity,
privileged the algebraic method. This
method consists in replacing the equation to
the partial derivatives that conditions the
distribution of the concentrations by an
algebraic equation in which one takes into
account the phenomena physics of diffusion
and transportation through the intermediary
of coefficients bound downwind to the
distance, the stability and to the conditions
of broadcasts to the air atmosphere. The
method Gaussian is based on the hypothesis
of the stationeries. To introduce in the
numerical solutions of ordinary partial
differential equations using examples from
climate modeling; and, to use and apply
Matlab as a mathematical-numerical tool.
2. Approaches Mathematical
Physical
Atmospheric dispersion modeling refers to
the mathematical description of contaminant
transport in the atmosphere, physical and
chemical processes have to be described by
mathematical terms in the beginning of the
development of a continental air pollution
model [1, 5]. These processes are: horizontal
transport (advection), horizontal diffusion,
chemical transformations in the atmosphere
combined with emissions from different
sources, deposition of pollutants to the
surface, and vertical exchange (containing
both vertical transport and vertical
diffusion). The dispersion models are used
to estimate or to predict the downwind
concentration of air pollutants or toxins
emitted from sources such as industrial
plants, vehicular traffic or accidental
chemical releases. The partial differential
equation to be solved is the classical
advection dispersion equation extended with
source sink terms to account for the sorption
and degradation processes; the advection-
diffusion equation reduces to
(1)
The height difference between the virtual
source and the real source is called the
plume height. Due to the transient
conditions in which the particles is liberated
to the atmosphere, and being the dispersion
a three-dimensional phenomena, transient
results of concentration are generated for a
fixed height plane of interest (z).
The elevation phenomenon occurs as a
function of wind velocity. Consider the
numerical solution of the advection -
dispersion equation assuming that D=0. In
this case there is only advection without any
physical dispersion/diffusion
. .( )u C K c Q R
C
t
International Journal of Chemical Engineering and Materials
DOI: 10.37394/232031.2023.2.5
Mohammedi Ferhat,
Haddad Hanane, Laggoun Chouki