Theoretical information about species transport and finite-rate chemistry as related to volumetric reactions is presented in this section. This information is organized in the following sections:
For more information about using species transport and finite-rate chemistry as related to volumetric reactions, see Volumetric Reactions in the User's Guide.
When you choose to solve conservation equations for chemical
species, Ansys Fluent predicts the local mass fraction of each species, , through the
solution of a convection-diffusion equation for the
th species. This conservation equation takes the following general
form:
(7–1) |
An equation of this form will be solved for species where
is the total number of fluid phase chemical species present in the
system. Since the mass fraction of the species must sum to unity, the
th mass fraction is determined as one minus the sum of
the
solved mass fractions. To minimize numerical error, the
th species should be selected as that species with the
overall largest mass fraction, such as
when the oxidizer is air.
In Equation 7–1, is the diffusion flux of species
, which arises due to gradients
of concentration and temperature. By default, Ansys Fluent uses the
dilute approximation (also called Fick’s law) to model mass
diffusion due to concentration gradients, under which the diffusion
flux can be written as
(7–2) |
where
For certain laminar flows, the dilute approximation may not be acceptable, and full multicomponent diffusion is required. In such cases, the Maxwell-Stefan equations can be solved; see Full Multicomponent Diffusion in the User's Guide for details.
Equation 7–2 is strictly valid when the mixture composition
is not changing, or when is independent of composition. This is an acceptable
approximation in dilute mixtures when
, for all
except the carrier gas. Ansys Fluent can also compute the
transport of non-dilute mixtures in laminar flows by treating such mixtures as
multicomponent system. Within Ansys Fluent,
can be specified in a variety of ways, including by specifying
, the binary mass diffusion coefficient of species
in species
.
is not used directly, however; instead, the diffusion
coefficient in the mixture,
, is computed as [299]:
(7–3) |
where and
are the mole fraction and mass fraction of species
, respectively, and
is the porosity. You can input
or
for each chemical species, as described in Mass Diffusion Coefficient Inputs in the Fluent User's Guide.
In turbulent flows, Ansys Fluent computes the mass diffusion in the following form:
(7–4) |
where is the turbulent viscosity, and
is the turbulent Schmidt number calculated as:
(7–5) |
where is the turbulent diffusivity. The default value of
is 0.7. Note that turbulent diffusion generally overwhelms
laminar diffusion, and the specification of detailed laminar diffusion
properties in turbulent flows is generally not necessary.
In turbulent flows, the total diffusion is the sum of the laminar diffusion
given by Equation 7–3 and the turbulent
diffusion given by Equation 7–5
A careful treatment of chemical species diffusion in the species transport and energy equations is important when details of the molecular transport processes are significant (for example, in diffusion-dominated laminar flows). As one of the laminar-flow diffusion models, Ansys Fluent has the ability to model full multicomponent species transport.
For multicomponent systems, it is not possible, in general, to derive
relations for the diffusion fluxes containing the gradient of only one
component (as described in Mass Diffusion in Laminar Flows). Here, the
Maxwell-Stefan equations will be used to obtain the diffusive mass flux.
This will lead to the definition of generalized Fick’s law diffusion
coefficients [649]. This method is preferred
over computing the multicomponent diffusion coefficients since their
evaluation requires the computation of co-factor determinants of size
, and one determinant of size
[636], where
is the number of chemical species.
From Merk [436], the Maxwell-Stefan equations can be written as
(7–6) |
where, | |
| |
| |
| |
|
For an ideal gas the Maxwell diffusion coefficients are equal to the
binary diffusion coefficients. If the external force is assumed to be the
same on all species and that pressure diffusion is negligible, then
. Since the diffusive mass flux vector is
, the above equation can be written as
(7–7) |
After some mathematical manipulations, the diffusive mass flux vector,
, can be obtained from
(7–8) |
where is the mass fraction of species
. Other terms are defined as follows:
(7–9) |
where, | |
| |
| |
| |
|
The solver will use a modification of the Chapman-Enskog formula [421] to compute the diffusion coefficient (cm2/s) using kinetic
theory:
(7–10) |
where, | |
| |
| |
| |
|
is a function of the dimensionless temperature
, which is calculated as:
(7–11) |
where is the temperature (in Kelvin).
is the Boltzmann constant, which is defined as the gas
constant,
, divided by Avogadro’s number.
in Kelvin for the mixture is the
geometric average:
(7–12) |
The relation between and
is obtained from the tabulation values given in [248], which is approximated in Ansys Fluent as:
(7–13) |
For a binary mixture, (in angstroms, where 1 angstrom =
1.0*10-10 m) is calculated as the
arithmetic average of the individual
s:
(7–14) |
The laminar mass diffusivity of all species is calculated as:
where denotes the mass diffusivity of species
in the mixture,
is the thermal conductivity,
is the mixture density, and
is the mixture specific heat.
Anisotropic species diffusion in porous media is modeled as follows:
For Fickian diffusion, the mass flux vector of species
is modeled as,
(7–15)
where
is the porosity,
is the anisotropic diffusion matrix in the porous zone, and the remaining nomenclature is the same as in Equation 7–4.
The full multi-component (Maxwell-Stefan) anisotropic diffusion flux vector is calculated similar to Equation 7–8 as,
(7–16)
The thermal diffusion coefficients can be defined as constants, polynomial functions, user-defined functions, or using the following empirically-based composition-dependent expression derived from [327]:
(7–17) |
This form of the Soret diffusion coefficient will cause heavy molecules to diffuse less rapidly, and light molecules to diffuse more rapidly, towards heated surfaces.
For many multicomponent mixing flows, the transport of enthalpy due to species diffusion
can have a significant effect on the enthalpy field and should not be neglected. In particular, when the Lewis number
(7–18) |
for any species is far from unity, neglecting this term can
lead to significant errors. Ansys Fluent will include this term by default.
In Equation 7–18, is the thermal conductivity.
For the pressure-based solver in Ansys Fluent, the net transport of species at inlets consists of both convection and diffusion components. For the density-based solvers, only the convection component is included. The convection component is fixed by the user-specified inlet species mass fraction. The diffusion component, however, depends on the gradient of the computed species field at the inlet. Thus the diffusion component (and therefore the net inlet transport) is not specified a priori. For information about specifying the net inlet transport of species, see Defining Cell Zone and Boundary Conditions for Species in the User’s Guide.
The reaction rates that appear as source terms in Equation 7–1 are computed in Ansys Fluent, for turbulent flows, by one of three approaches:
Direct use of finite-rate kinetics: The effect of turbulent fluctuations on kinetics rates are neglected, and reaction rates are determined by general finite-rate chemistry directly.
Eddy-dissipation model: Reaction rates are assumed to be controlled by the turbulence, ignoring the effect of chemistry timescales, which avoids expensive Arrhenius chemical kinetic calculations. The model is computationally cheap, but, for realistic results, only one or two step heat-release mechanisms should be used. This approach should be used only when the chemistry timescales of interest are known to be fast relative to the turbulence timescales throughout the domain.
Eddy-dissipation-concept (EDC) model: Detailed chemical kinetics can be incorporated in turbulent flames, considering timescales of both turbulence and kinetics. Note that detailed chemical kinetic calculations can be computationally expensive.
The generalized finite-rate formulation is suitable for a wide range of applications including laminar or turbulent reaction systems, and combustion systems with premixed, non-premixed, or partially-premixed flames.
When no turbulence-chemistry interaction (TCI) model is used, finite-rate kinetics are incorporated by computing the chemical source terms using general reaction-rate expressions, without attempting to account explicitly for the effects of turbulent fluctuations on the source-term calculations. This approach is recommended for laminar flows, where the formulation is exact, or for turbulent flows using complex chemistry where either the turbulence time-scales are expected to be fast relative to the chemistry time scales or where the chemistry is sufficiently complex that the chemistry timescales of importance are highly disparate.
The net source of chemical species due to reaction is computed as the sum of the reaction sources
over the
reactions that the species participate in. For reactions in a
porous medium, the net source due to reactions is obtained by multiplying the
reaction rates with porosity:
(7–19) |
where is the molecular weight of species
,
is the porosity, and
is the molar rate of creation/destruction of species
in reaction
. Reaction may occur in the continuous phase at wall
surfaces.
Consider the
th reaction written in
general form as follows:
(7–20) |
where, | |
| |
| |
| |
| |
| |
|
Equation 7–20 is valid for both reversible
and irreversible reactions. For irreversible reactions, the backward
rate constant, , is zero.
The summations in Equation 7–20 are for all chemical species in the system, but only species that appear as reactants or products will have nonzero stoichiometric coefficients.
The molar rate of creation/destruction of species in reaction
is given by
(7–21) |
where, | |
| |
| |
|
Note that the rate exponent for the reverse reaction part in
Equation 7–21 is the product species stoichiometric
coefficient ().
For information on more general reaction mechanisms in CHEMKIN format, see Getting Started with Ansys Chemkin. For information about inputting the stoichiometric coefficients and rate exponents within the Ansys Fluent user interface, for both global forward (irreversible) reactions and elementary (reversible) reactions, see Inputs for Reaction Definition in the Fluent User's Guide. The information below refers to mechanisms manually entered in Ansys Fluent.
represents the net effect of third bodies
on the reaction rate. This term is given by
(7–22) |
where is the third-body efficiency
of the
th species in the
th reaction. By default, Ansys Fluent does not include third-body
effects in the reaction rate calculation. You can, however, opt to
include the effect of third-body efficiencies if you have data for
them.
The forward rate constant for reaction ,
, is computed using
the Arrhenius expression
(7–23) |
where, | |
| |
| |
| |
|
You (or the database) will provide values for ,
,
,
,
,
,
, and, optionally,
during the problem
definition in Ansys Fluent.
If the reaction is reversible, the backward rate constant for
reaction ,
, is computed, by default, from the forward rate
constant using the following relation:
(7–24) |
where is the equilibrium constant
for the
th reaction, computed
from
(7–25) |
where denotes
atmospheric pressure (101325 Pa). The term within the exponential
function represents the change in Gibbs free energy, and its components
are computed as follows:
(7–26) |
(7–27) |
where and
are the entropy and enthalpy of the
th species
evaluated at temperature
and atmospheric pressure. These values are specified
in Ansys Fluent as properties of the mixture material.
Ansys Fluent also provides the option to explicitly specify the
reversible reaction rate parameters (pre-exponential factor, temperature
exponent, and activation energy for the reaction) if desired. In this
case, the backward rate constant of the reversible reaction is computed using the relationship
similar to Equation 7–23:
(7–28) |
where, | |
| |
| |
|
For more information about specifying the backward reaction rate parameters, see Inputs for Reaction Definition in the Fluent User's Guide.
General formulations for pressure-dependent reactions are available through use of CHEMKIN imported mechanisms and detailed descriptions of these formulations can be found in Getting Started with Ansys Chemkin. If you choose to manually enter reaction expressions through the Ansys Fluent interface, Ansys Fluent can use one of three methods to represent the rate expression in pressure-dependent (or pressure fall-off) reactions. These are a subset of the formulations available through use of CHEMKIN imported mechanisms. A “fall-off” reaction is one in which the temperature and pressure are such that the reaction occurs between Arrhenius high-pressure and low-pressure limits, and therefore is no longer solely dependent on temperature.
There are three methods of representing the rate expressions in this fall-off region. The simplest one is the Lindemann [377] form. There are also two other related methods, the Troe method [206] and the SRI method [634], that provide a more accurate description of the fall-off region.
Arrhenius rate parameters are required for both the high- and
low-pressure limits. The rate coefficients for these two limits are
then blended to produce a smooth pressure-dependent rate expression.
In Arrhenius form, the parameters for the high-pressure limit () and the low-pressure limit
(
)
are as follows:
(7–29) |
(7–30) |
The net rate constant at any pressure is then taken to be
(7–31) |
where is defined as
(7–32) |
and is the concentration of the bath gas, which
can include third-body efficiencies. If the function
in Equation 7–31 is unity, then this is the Lindemann
form. Ansys Fluent provides two other forms to describe
, namely the Troe method
and the SRI method.
In the Troe method, is given by
(7–33) |
where
(7–34) |
and
(7–35) |
The parameters ,
,
, and
are specified as inputs.
In the SRI method, the blending function is approximated as
(7–36) |
where
(7–37) |
In addition to the three Arrhenius parameters for the low-pressure
limit ()
expression, you must also supply the parameters
,
,
,
, and
in the
expression.
For Chemically Activated Bimolecular pressure dependent reactions, the net rate constant at any pressure is
(7–38) |
Important: Chemical kinetic mechanisms usually contain a wide range of time scales and form a set of highly nonlinear, stiff coupled equations. For solution procedure guidelines, see Solution Procedures for Chemical Mixing and Finite-Rate Chemistry in the User’s Guide. Also, if you have a chemical mechanism in CHEMKIN [300] format, you can import this mechanism into Ansys Fluent. See Importing a Volumetric Kinetic Mechanism in CHEMKIN Format in the User's Guide.
Under some combustion conditions, fuels burn quickly and the overall rate of reaction is controlled by turbulent mixing. In high-temperature non-premixed flames, for example, turbulence slowly convects/mixes fuel and oxidizer into the reaction zones where they burn quickly. In certain premixed flames, the turbulence slowly convects/mixes cold reactants and hot products into the reaction zones, where reaction occurs rapidly. In such cases, one approximation is to assume the combustion is mixing-limited, allowing neglect of the complex chemical kinetic rates and instead assuming instantaneous burn upon mixing.
For mixed-is-burned approximation, Ansys Fluent provides a
turbulence-chemistry interaction model, based on the work of Magnussen
and Hjertager [410], called the eddy-dissipation
model. With this model, the net rate of production of species due to reaction
,
, is given by the smaller
(that is, limiting value) of the two expressions below:
(7–39) |
(7–40) |
where, | |
| |
| |
| |
|
In Equation 7–39 and Equation 7–40, the chemical reaction rate is governed
by the large-eddy mixing time scale, , as in the eddy-breakup model of Spalding [624]. Combustion proceeds whenever turbulence is
present (
), and an ignition source is not required to initiate
combustion. This is usually acceptable for non-premixed flames, but
in premixed flames, the reactants will burn as soon as they enter
the computational domain, upstream of the flame stabilizer. To remedy
this, Ansys Fluent provides the finite-rate/eddy-dissipation model,
where both the finite-rate reaction rates (Equation 7–21), and eddy-dissipation (Equation 7–39 and Equation 7–40) rates are calculated. The net reaction rate is taken as the minimum
of these two rates. In practice, the finite-rate kinetics acts as
a kinetic “switch”, preventing reaction before the flame
holder. Once the flame is ignited, the eddy-dissipation rate is generally
smaller than the Arrhenius rate, and reactions are mixing-limited.
Important:
Although Ansys Fluent allows multi-step reaction mechanisms (number of reactions
) with the eddy-dissipation and finite-rate/eddy-dissipation models, these will likely produce incorrect solutions. The reason is that multi-step chemical mechanisms are typically based on Arrhenius rates, which differ for each reaction. In the eddy-dissipation model, every reaction has the same, turbulent rate, and therefore the model should be used only for one-step (reactant → product), or two-step (reactant → intermediate, intermediate → product) global reactions. The model cannot predict kinetically controlled species such as radicals. To incorporate multi-step chemical kinetic mechanisms in turbulent flows, use the EDC model (described in The Eddy-Dissipation Model for LES).
The eddy-dissipation model requires products to initiate reaction (see Equation 7–40). When you initialize the solution for steady flows, Ansys Fluent sets all species mass fractions to a maximum in the user-specified initial value and 0.01. This is usually sufficient to start the reaction. However, if you converge a mixing solution first, where all product mass fractions are zero, you may then have to patch products into the reaction zone to ignite the flame. For details, see Ignition in Steady-State Combustion Simulations in the User’s Guide.
When the LES turbulence model is used, the turbulent mixing
rate, in Equation 7–39 and
Equation 7–40, is replaced by the subgrid-scale
mixing rate. This is calculated as
(7–41) |
where, | |
| |
|
The eddy-dissipation-concept (EDC) model is an extension of the eddy-dissipation model that
allows inclusion of detailed chemical mechanisms in turbulent flows [409]. It assumes that reactions occur within small
turbulent structures, called the fine scales. These fine scales occupy a
fraction of the computational cell, characterized by a volume fraction
. Combustion at the fine scales is assumed to occur as a
constant pressure reactor, with initial conditions taken as the current species
and temperature in the cell. Reactions proceed over the time scale
, governed by the reaction rates of Equation 7–21, and are integrated numerically using an
ODE solver. The source term in the conservation equation for the mean species
, Equation 7–1, is modeled
as
(7–42) |
where is the fine-scale species mass fraction after reacting over
the time scale
.
The EDC model can incorporate detailed chemical mechanisms into turbulent reacting flows. However, typical mechanisms are invariably stiff and their numerical integration is computationally costly. Hence, the model should be used only when the assumption of fast chemistry is invalid, such as modeling low-temperature or high-pressure combustion, the slow CO burnout in rapidly quenched flames, or the NO conversion in selective non-catalytic reduction (SNCR).
For guidelines on obtaining a solution using the EDC model, see Solution of Stiff Chemistry Systems in the User's Guide.
In the standard EDC model [217], the volume fraction of the reactive fine scales is modeled as:
(7–43) |
where the length scale is computed as:
(7–44) |
where
| |
| |
| |
|
The integration time scale is modeled as:
(7–45) |
where is a time scale constant equal to 0.4082.
The standard EDC model (see The Standard EDC Model
for details), has been successfully applied in modeling turbulence-chemistry
coupling by incorporating detailed chemical mechanisms. However, the main
shortcoming of the standard EDC model is that neither the length scale
constant nor the time scale constant
depends on local flow and chemistry variables. Studies
have shown limitations of the standard EDC model. For example, when applied
to the simulation of Moderate and Intense Low-oxygen Dilution (MILD) systems
(slow chemistry due to strong oxygen dilution), the EDC model gives a
significant overestimation of temperature levels [361], [362].
Several authors have offered the generalization of the EDC model for applications to a wider flame regime. The Partially Stirred Reactor (PaSR) model [176], [720] has been applied to both mild and supersonic combustions. It is conceptually similar to the standard EDC model, but is characterized by a different definition of the reacting volume fraction and time scale:
(7–46) |
(7–47) |
In Equation 7–46, is defined as:
(7–48) |
In Ansys Fluent, the chemistry time scale is computed based upon the practice outlined in [166]:
(7–49) |
where are the reaction rates (in
kg/m3/s) of CH4,
H2, O2,
H2O, and CO2 as these
slower major species dominate the fine-scale time-scales and larger flame
structure.
The mixing time scale is taken as a fraction of the integral time scale of
turbulence
:
(7–50) |
where can be a constant value or a function of the local
turbulent Reynolds number (
):
(7–51) |
where is the constant of the k-ε turbulence model.
When Equation 7–51 is used to compute , the model is referred to as the fractal method [176]. The exponent coefficient
is expressed as:
(7–52) |
where is the fractal dimension. A value of
= 3 corresponds to the Kolmogorov time-scale, whereas a
value of
= 5 results in the integral time.
Note that when the LES turbulence model is used, is computed from the geometric mean of the Kolmogorov time
scale and the turbulence time scale [366].
Premixed flames have typical laminar flame thicknesses of the order of a millimeter. Since the laminar flame propagation speed is determined by species diffusion, heat conduction and chemical reaction within the flame, sufficient grid resolution inside the flame is necessary to predict the correct laminar flame velocity. In contrast, the combustor dimensions are usually much larger than the laminar flame thickness and the flame cannot be affordably resolved, even with unstructured and solution-adaptive grids.
The premixed laminar flame speed, denoted , is proportional to
where
is a diffusivity and
is a reaction rate. The laminar flame thickness is
proportional to
. Hence, the laminar flame can be artificially thickened,
without altering the laminar flame speed, by increasing the diffusivity and
decreasing the reaction rate proportionally. The thickened flame can then be
feasibly resolved on a coarse mesh while still capturing the correct laminar
flame speed.
The thickening factor is calculated in Ansys Fluent as:
(7–53) |
where is the grid size,
is the laminar flame thickness, and
is the user-specified number of points in the flame (default
of 8). The grid-size,
, is determined as
where
is the cell volume and
is the spatial dimension (2 or 3). The laminar flame
thickness,
, is a user-input, and may be specified as a constant, a
User-Defined Function, or calculated as
, where
is the thermal diffusivity evaluated as
(
is the thermal conductivity,
is the density and
is the specific heat).
All species diffusion coefficients, as well as the thermal conductivity, are multiplied by the
thickening factor, , and all reaction rates are divided by
. However, away from the flame, these enhanced diffusivities
can cause erroneous mixing and heat-transfer, so the flame is dynamically
thickened only in a narrow band around the reaction front. This band is
calculated by multiplying
with, a factor
calculated as
(7–54) |
In Equation 7–54, is the spatially filtered absolute
value of the reaction rate, and
is a constant with a default value of 10.
The absolute reaction rate is filtered several times, and
is the maximum value of
in the domain.
ranges from unity in
the band around the flame to zero outside this band.
The Thickened Flame Model (TFM) [497] is most often used with a single step chemical mechanism where the global reaction has been tuned to provide the correct laminar flame speed. The TFM can, in principal, be used with multi-step reaction mechanisms, however all composition profiles should be adequately resolved within the flame. The TFM is available in both the pressure-based as well as density-based solvers.
While the TFM can be used to model laminar flames, its most common application is as an LES combustion model for turbulent premixed and partially-premixed flames. The turbulent flame speed of a premixed flame is determined principally by the flame wrinkling, which increases the flame surface area.
The thickening of the flame alters its interaction with the turbulence. This
should be considered in the calculations of the species formation and
destruction rates. As the flame thickens, the ability of turbulence to wrinkle
the flame diminishes, which impacts the turbulent flame speed propagation. The
decrease in the turbulence chemistry interaction is compensated by multiplying
the reaction rates by the efficiency function . In Ansys Fluent, the Charlette and Colin efficiency functions are
available for modeling this phenomenon.
The Colin efficiency function is computed by:
(7–55) |
where, | |
| |
| |
| |
| |
|
(7–56) |
where, | |
| |
| |
|
The turbulent Reynolds number in Equation 7–56 is based on the integral
length scales
and the RMS velocity fluctuations at integral length scales.
The integral length scale is the length of the largest eddies present in the
domain. It depends on the geometry, and a value of 1/4 to 1/2 of a
characteristics dimension (such as a burner diameter, an inlet diameter, or a
size of a bluff body) is typically used. The RMS velocity fluctuations at the
integral length scale is computed as:
(7–57) |
where is the RMS velocity at the integral length scale
.
(7–58) |
Here, the superscript 0 refers to the flame without thickening, and the superscript 1 refers to the thickened flame.
When the flow is laminar, equals 0, and the Colin efficiency function is reduced to 1.
When the turbulent velocity fluctuations vary, such that
(7–59) |
the Colin efficiency function approaches a theoretical maximum limit:
(7–60) |
The Charlette efficiency function [100], [687] is computed as follows:
(7–61) |
where
is calculated as:
(7–62) |
with = 1.4, and
(7–63) |
(7–64) |
(7–65) |
(7–66) |
In the above equations, is the Kolmogorov constant with a value of 1.5.
All species reaction rates are multiplied by . The effective species diffusivities (and thermal
conductivity) in each cell are dynamically determined as:
(7–67) |
where is
the molecular (laminar) diffusivity and
is the turbulent diffusivity.
may be computed with any of the available methods
in Ansys Fluent, including kinetic theory and User Defined Functions (UDFs).
Since the kinetic coefficients of 1-step reactions are invariably
adjusted to capture the actual laminar flame speed, the same transport
properties that are used in this tuning simulation should be used
in the TFM simulation. In the narrow band around the flame where
is one, the turbulent
diffusivities are switched off and the molecular diffusivities are
enhanced by a factor
. Away from the flame where
is zero, the effective diffusivity
is the non-thickened value of
.
When using the finite-rate (FR) chemistry, or when using eddy-dissipation
(ED), finite-rate/eddy-dissipation (FR/ED) or EDC model, as described
above, chemical species evolve according to the prescribed kinetic
mechanism. In the Relaxation to Chemical Equilibrium model, the species
composition is driven to its equilibrium state. The reaction source
term in the
th mean species conservation
equation (Equation 7–1), is modeled
as
(7–68) |
where, | |
| |
| |
superscript | |
|
Equation 7–68 implies that
species react toward their chemical equilibrium state over the characteristic
time, , as in the Characteristic Time model [320]. Since chemical equilibrium does not depend on reactions
or reaction rates, for a given
, the reaction source term in Equation 7–68 is independent of the reaction
mechanism.
The Relaxation to Chemical Equilibrium model is an option available for any of the turbulence-chemistry interaction options. When no turbulence-chemistry model is used, the characteristic time is calculated as
(7–69) |
where is a convection/diffusion time-scale in a cell.
is a cell chemical time-scale modeled as
(7–70) |
In Equation 7–70, is a model constant (default of 1), index
denotes the user-specified
fuel species,
is the fuel species mass fraction, and
is
the rate of change of the fuel species mass fraction, while
denotes
the minimum over all specified fuel species. Hence,
represents a chemical ignition time-scale
for the fuel species, and is used to prevent a premixed flame from
auto-igniting, similar to the FR/ED model. Note that a kinetic mechanism
is required to evaluate
.
For the ED model, the characteristic time-scale is evaluated as , where the turbulent time-scale is
, and the default turbulent rate constant is
. For the FR/ED model, the characteristic time-scale is
calculated as
. Typically, the ED and FR/ED models employ a 1-step reaction,
or a 2-step reaction where hydrocarbons pyrolize to CO, which then oxidizes to
CO2. The Relaxation to Chemical Equilibrium model can
be considered as an extension of the ED type models where species react towards
chemical equilibrium instead of complete reaction. The model should provide more
accurate predictions of intermediate species such as CO and radicals required
for NOx modeling such as O and OH.
Since chemical equilibrium calculations are typically less computationally expensive than detailed chemistry simulations, the Relaxation to Chemical equilibrium can be used to provide a good initial condition for full-kinetic steady-state simulations. The model can also be used in lieu of the Eddy-Dissipation model where the solution tends to chemical equilibrium instead of complete reaction.
The assumption of chemical equilibrium can lead to large errors
in rich zones for hydrocarbon fuels. Ansys Fluent offers the option of
reducing the reaction rate in Equation 7–68 by increasing the characteristic time-scale in rich zones. With this option, the local
equivalence ratio in a cell is calculated as
(7–71) |
where ,
, and
denote the atomic molar fraction of oxygen, hydrogen and
carbon. The time-scale,
, is then multiplied by a factor
when the local equivalence ratio
exceeds the specified rich equivalence ratio
. The default rich equivalence ratio is 1, and the default
exponential factor,
, is 2. The option to enable the slow reaction rate in rich
mixtures is available in the text interface.
Since chemical equilibrium calculations can consume computational
resources, ISAT tabulation is the recommended (and default) solution
method. The initial Ansys Fluent iterations speed up significantly as
the table is built up with sufficient entries and the majority of
queries to the table are interpolated. Since chemical equilibrium
compositions are uniquely determined by the initial temperature, pressure
and elemental compositions of the mixture, the ISAT table dimensions
are for isobaric systems.
In most combustion cases, the number of elements is much smaller than
the number of chemical species, and the ISAT table is built up relatively
quickly. The Direct Integration option may also
be selected, in which case equilibrium calculations will always be
performed at all cells.
At hypersonic speeds, chemical reactions such as dissociation and recombination can have large impact on the flow. If the flow characteristic time and the chemical reaction time are of approximately the same order, the fluid element does not reside at one location long enough to bring the local chemical reactions to equilibrium, and therefore, the flow could be in locally chemical non-equilibrium. The two-temperature model can be used with the finite-rate chemistry model to simulate these thermal-chemical non-equilibrium flows.
When the two-temperature model is coupled with the finite-rate chemistry model to describe the thermal-chemical non-equilibrium phenomena in hypersonic flows, Equation 7–23 takes the form:
(7–72) |
where is the control temperature. The coefficient
for dissociation reactions, to account for the fact that
dissociative reactions are greatly influenced by the vibrational modes. For exchange
reactions, the coefficient
.
For details on specifying the control temperature coefficient, see Using the Two-Temperature Model in the Fluent User's Guide.