Khoshandam2005 PDF
Khoshandam2005 PDF
A mathematical model based on grain model, is carbon dioxide. The results show good agreement for
presented. The model considers dynamic changes of gas experimental conditions where both chemical kinetics
and solid concentrations and temperature in the pellet of and product layer diffusion are significant in the first
the solid reactant. In addition, structural changes of reaction and the reaction obeys a non-linear chemical
solid reactant (porosity and grain size changes) and kinetics in the second reaction.
diffusion of gaseous reactants through the product layer B. Khoshandam (E-mail: bkh@engineer.com) and R. V.
are considered. Effective diffusion coefficient is Kumar (for correspondence – E-mail: rvk10@cam.ac.uk) are
assumed to change with porosity in the pellet as a at the Department of Materials Science & Metallurgy,
quadratic function in the mass balance equation. University of Cambridge, New Museums Site, Pembroke
Effective heat capacity and conductivity are also Street, Cambridge CB2 3QZ, UK; E. Jamshidi (E-mail:
modelled as functions of porosity in the heat balance jamshidim@yahoo.com) is at the Department of Chemical
equation. The finite volume method has been selected Engineering, Amir-Kabir University (Tehran Polytechnic),
for solving mass and heat balance equations in the pellet Hafez Avenue, Tehran, Iran.
and the computations are done by a program developed © 2005 Institute of Materials, Minerals and Mining and
in MATLAB. The results of the program show good Australasian Institute of Mining and Metallurgy. Published
agreement in comparison with analytical solutions for by Maney on behalf of the Institutes. Manuscript received 28
both isothermal and non-isothermal systems. The model January 2004; accepted in final form 23 September 2004.
was used to simulate the reduction of cobalt oxide with Keywords: Simulation, non-catalytic gas–solid reactions,
methane and also the carbon gasification reaction with grain model, reduction of cobalt oxide with methane
INTRODUCTION that may form at the surface of each grain will offer
Non-catalytic gas–solid reactions are commonly increasing resistance to diffusion with time. The grain
encountered in many chemical and metallurgical model has been extensively employed in modelling of
processes. Reduction of metal oxides with reducing non-catalytic gas–solid reactions and applied to a
gases is a typical example in extractive metallurgy that number of systems such as reduction of nickel
is based on non-catalytic gas–solid reactions. A oxide,6–8 hydrofluorination of UO2,9 and reaction of
general type of non-catalytic gas solid reaction may be zinc oxide with hydrogen sulphide.10
represented as: In the present work, the grain model was applied
for the reduction of cobalt oxide pellets with methane.
A(gas) + bB(solid) → cC(gas) + dD(solid) (1)
A program was developed in MATLAB software that
There have been many papers published about is able to solve mass and heat balance equations in
simulation of such reactions in the last three decades. pellets considering both structural changes in the
Different simulation techniques and models have been pellet (such as grain radius and porosity), and
proposed and a good review is presented in the variations in the effective diffusion coefficient. In
literature.1–4 order to reduce computation time, matrix operation
Gas–solid reactions are normally carried out facilities in MATLAB have been used. These
between a gas phase and a collection of solid particles operations can minimise the number of loops applied
contained in a pellet. During gaseous diffusion in the program. The mass and heat balance equations
through a pellet, a chemical reaction may also occur. were discretised using finite volume method and were
The grain model introduced by Szekely et al.5 is solved in the implicit form. Both Patisson et al.11 and
fundamentally based on this idea. The grain model Liu and Bhatia12 used the finite volume method and a
also referred to as the particle-pellet model is based on semi-discrete Petrov-Galerkin finite element method,
the assumption that grains in a pellet are surrounded respectively; however, porosity change, grain product
by pores through which the gas must diffuse to arrive layer resistance, and effective diffusion coefficient
at a sharp interface between the grain particle and the variation as a function of porosity were not
gas phase for reaction to take place. A solid product considered.
C10 Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114 DOI 10.1179/037195505X39058
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114 C11
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
Table 1 Terms for mass balance equation in pellet Table 2 Terms for initial and boundary conditions of mass
balance equation in pellet
Term Definition
Term Definition
ε Porosity of pellet
CA Concentration of reducing agent A in pellet CA0 Initial concentration of reducing agent A in pellet
t Independent variable, time rp Pellet radius for spherical and cylindrical pellets and
z Independent variable, position in the pellet, radial half-thickness for flat pellets
position in spherical and cylindrical pellets and axial kc Convective mass transfer coefficient
CAb Concentration of A in bulk of gas stream
position in slab-like pellets
CAs Concentration of A on surface of pellet
Fp Pellet-shape factor, 1, 2 and 3 for infinite slab, long
cylinder and sphere, respectively
De Effective diffusion coefficient of A in pellet Table 3 Terms for mass balance equation through the
Fg Grain shape factor, 1, 2 and 3 for infinite slab, long product layer
cylinder and sphere, respectively
ε0 Initial porosity of pellet Term Definition
rc Radial position of reaction front in grain
CAi Concentration of A on reaction front
r0 Initial radius of grain DAp Diffusivity of A in the product layer around grains
fG Rate of surface reaction rg Radius of grain
equation for the solid reactant can be transformed to where ρD, MD, d and εD are density, molecular weight,
an equation for radius of the unreacted core of the stoichiometric coefficient and porosity of solid
grains in terms of Accumulation = Input – Output + product D, respectively.
Generation where Input – Output = 0:
drc =- M B bf Heat balance equation in a pellet – The heat balance
tB G (6)
dt equation for the pellet can be written in terms of
where MB, ρB and b are molecular weight, density and Accumulation = Input – Output + Generation, as
stoichiometric coefficient of solid reactant B, respectively. follows:
The initial condition for this equation is: 2 _ C pe T i
at t = 0, rc = r0 (7) =
2t
1 2 zF r F -1 g
z F - 1 2z
p
2z r0 g
K d _0 g
c i tB M D
g
C12 Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
where VP0 and VP are initial pellet volume and variable Table 6 Terms for the reaction rate laws
pellet volume, respectively.
Term Definition
Intraparticle diffusion coefficient is defined based
on the random pore model of Wakao and Smith:13 k Reaction rate constant
2
D e = D e0 c ff0 m
CB Concentration of solid reactant B
(17)
n, m Constant values
where De0 is initial effective diffusion coefficient of gas k1 A constant value
reactant in the pellet. k’ Frequency factor
Extent of reaction or conversion about non-porous Ea Activation energy of chemical reaction
grains is defined as local conversion and is the ratio of R Ideal gas constant
mass of solid product D produced at each time to
mass of solid product if the grain converts to solid
nd, the number of solid grains per unit volume of
product completely; so for grains:
Fg porous solid, is calculated from:
x = 1 - c rr0c m (18) 3 _1 - f i
nd = (26)
4rrg3
where x is conversion of the grain and is a function of
local place in the pellet and time. However, conversion The molecular diffusivity is obtained from the
of pellet is defined as overall conversion and is Chapman and Enskog equation.15
calculated from local conversion integration over the The gas viscosity for each component in the bulk of
pellet as: rp the gas can be calculated and the bulk viscosity can be
# z F - 1 xdz
p
obtained using ‘rule of mixtures’.
X = 0 rp (19) The effective specific heat capacity and thermal
# z F - 1 dz p
conductivity of the pellet, respectively, can be
0
where X is overall conversion in pellet and is a obtained from:
function of time and rp is radius of the pellet for
C p = _1 - f i C p + fC p
e s g (27)
spherical and cylindrical pellets and half-thickness for
flat pellets. 2
K e = _1 - f i K s + f 2 K g (28)
Expression of the reaction rate law where CPs and CPg are the specific heat capacity of
The surface reaction rates can be defined as a power solid and gas, respectively, in the pellet and Ks and Kg
equation: are the thermal conductivity of solid and gas in the
pellet, respectively.
f G = kC An C Bm (20)
The convective mass transfer coefficient, kc, can be
and Langmuir-Hinshelwood equation is given by: calculated from the equation used for Sherwood number
(Sh = kc dp/DAM). In general, the dimensionless
f G = kC A (21)
1 + k1 C A Sherwood number can be expressed as a function of
The Arrhenius equation is obtained by considering Reynolds number (Re = ρf u∞ dp/µf) and the Schmidt
temperature effect on the reaction rate as: number (Sc = µf/ρf DAM) with a specific empirical
Ea equation being valid for a given geometrical situation
k = k le - RT (22)
and for a given range of parameters. For example, for a
where the terms are defined in Table 6. laminar flow (0 < Re < 200) past a spherical pellet, the
correlation of Ranz and Marshall,16 is:
Expression of parameters
Sh = 2 + 0.6Re 1 2 Sc 1 3
(29)
The effective diffusivity may be obtained with the aid
of the Bosanquet interpolation formula: In these equations, µf, ρf and u∞ are viscosity, density
-1 and velocity of gas stream, respectively, and dp is
f
De = c x m c D1AM + D1AK m (23) diameter of pellet.
where DAM and DAK are molecular diffusivity and Table 7 Terms for general equation for transport of a scalar
Knudsen diffusivity of gaseous reactant A in the pellet parameter Φ
and τ is tortuosity coefficient of the pellet.
Term Definition
The Knudsen diffusivity is calculated from:
Φ A scalar parameter such as concentration or temperature
1 2
CV Control volume
DK = 4 c r
8RT ko (24)
3 MAm ∆t Time step
dV Volume element
where k0 is calculated from the ‘dusty gas model’ of
dA Surface element
Mason et al.:14
n Outward normal vector to surface element dA
Γ
k 0- 1 = c 128 m n d rg2 c1 + r m
Diffusion coefficient
(25)
9 8 SΦ Source term
Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114 C13
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
In an analogous manner, the convective heat temperature as given by Equations (3) and (13). In
transfer coefficient also can be calculated from a each time level, all dependent parameters are also
similar equation used for laminar flow past a sphere: renewed. Next, the solution T and CA are assigned to
T0 and CA0 and the procedure is repeated to progress
Nu = 2 + 0.6Re 1 2 Pr 1 3
(30)
the solution by a further time step.
where Pr is the Prandtl number (Pr = CPf µf/Kf) and
Nu is the Nusselt number (Nu = hc dp/Kf). In these
equations, CPf and Kf are the specific heat capacity and PROGRAM SPECIFICATIONS
thermal conductivity of the gas stream, respectively. The program developed in MATLAB included 12
The experimental conditions are so chosen, in our sections.
work, that Sh and the Nu both tend to infinity, (i) Data input. The data needed for the program
implying rapid mass and heat transfer by convection included the state of the governing equation
in the gas phase. In this manner, the model can be (steady, unsteady isothermal or non-isothermal
tested for selected limiting conditions. state), boundary type (constant value at boundary
[Dirichlet] or a relation between first derivative and
value of parameter at boundary [Neumann]), grain
NUMERICAL METHOD and pellet specifications (weight, geometry, shape
The finite volume integration of partial differential factors), operating conditions (temperature,
Equations (2) and (12), over a control volume (CV) pressure, volume percentage of reducing agent in
with a further integration over a finite time step is the carrier gas, total flow rate, reactor diameter),
applied for the discretisation process of the equations. physical properties of carrier gas, reaction
For transport of a scalar parameter Φ, we obtain:17 components and products (molecular weight,
t + Dt
density, specific heat capacity, heat conductivity),
#d # 2 tU i dt dV = chemical reaction information (stoichiometric
2t _ n
CV t
coefficients), and diffusivity of gaseous reactant
t + Dt t + Dt
through the product layer. In addition for the
# d # n. _ CgradU i dA n dt + # # S U dVdt (31)
t A t CV numerical solution, number of increments in space
where the terms are defined in Table 7. domain, time step and final time should be given
The accumulation term has been discretised using a to the program.
first order backward differencing scheme. Indeed, for (ii) Necessary parameters calculation. In this
the diffusion term, we apply central differencing. The section, parameters needed for running of the
source term, SΦ, can be approximated by means of a program are calculated. These parameters
linear form: consist of: initial porosity, effective heat capacity
and effective conductivity of the pellet,
# S U dV = SU DV = S u + S p U p (32)
CV tortuosity factor, bulk concentration of reducing
where SU is the average of source term in control gas, viscosity of gas mixture, effective diffusivity
volume, Su and Sp are constant values and Φp is of reactant gas through the pellet, Sherwood
parameter Φ in node p inside the control volume. and Nusselt numbers.
The explicit discretisation of equations is very (iii) Chemical reaction rate function. Two rate models
expensive to improve spatial accuracy because can be selected, power equation and Langmuir-
maximum possible time step has to be drastically Hinshelwood equation.
reduced. The two schemes, Crank-Nicolson and fully (iv) Solution of mass balance equation in pellet. In
implicit, have been applied for the discretisation this section, all matrices coefficients according
process. For a general control volume with left-side to the finite volume technique are made and
and right-side face positions of Xw and Xe, then algebraic sets of equations are solved using
respectively, in the Crank-Nicolson scheme, where De matrix operation facilities in MATLAB.
or Ke is constant and a uniform grid spacing, ∆X, we (v) Solution of reaction front equation or mass
have to use time steps as: balance equation for solid reactant. In this
2f _ DX i_ X eF p +1
- X wF + 1i
p section, radius of unreacted core in grain are
Dt < (33) calculated in each time step.
D e _ X eF + X wF i_ Fp + 1i
p p
C14 Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
a b
2 (a) Effect of grain radius on conversion–time curve. (b) Effect of grain shape factor on conversion–time curve, Fg
= 1 (slab grains), Fg = 2 (cylindrical grains) and Fg = 3 (spherical grains)
(x) Calculation of porosity of pellet. temperature range was 800–950°C. The details of
(xi) Parameter refinement. In this section, all parameters experimental conditions have been described by
such as source term of equation and effective Khoshandam.18 Frequency factor, k′ = 1755·5 m/s and
diffusion coefficient are renewed. The procedure of activation energy, Ea = 155·6 kJ/mol for this reaction
sections (i) to (iv) is repeated for the next time step. were derived from kinetic studies.
(xii) Result visualisation and report file generation.
Finally, in this section, conversion-time plot, Effect of grain size specifications
other necessary 2- or 3-dimensional plots and The effect of grain size has been evaluated by the
report files are generated. model for a slab-like pellet made up of spherical
grains, Fp = 1, Fg = 3 (Fig. 2a). As the radius of the
grain increases, the time needed for completing the
RESULTS OF THE MODEL reaction is increased. For a slab pellet with 3 mm
In this section, effects of changing several important thickness (rp = 1·5 mm), the time taken to achieve
parameters in gas–solid reaction simulation have been 100% conversion has increased from 1·7 x 103 s to 4·5
considered. The isothermal model and kinetic x 103 s, as the radius of the grain sphere is increased
parameters similar to reduction of cobalt oxide (CoO) from 2·5 µm to 10 µm. This behaviour has been seen
with methane have been used for verifying parameters. in a number of reduction reactions. For example, the
The reduction of cobalt oxide with methane is as rate of reduction of nickel oxide by hydrogen is shown
follows: to increase due to grinding of nickel oxide.19 The shape
of grains also has been changed and its effect on the
CH4 + CoO → CO + 2 H2 + Co (35)
conversion–time curve was evaluated by the model.
We studied the kinetics of this reaction by Figure 2b shows the effect of grain shape factor
thermogravimetry, using synthetic porous pellets of variation for a slab-like pellet (Fp = 1). Spherical
pure CoO and various CH4 + Ar mixtures. The grains (Fg = 3) show higher conversion and shorter
a b
3 a) Effect of shape factor change, Fp = 1 (dashed line), Fp = 2 (dashed line), Fp = 3 (solid line) and (b) pellet
porosity change on the simulation shown for a slab-like pellet with spherical grains
Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114 C15
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
a b
c d
e f
g h i
4 Effect of changing initial porosity of pellet on the simulation (a), on gas reactant profile in the pellet, porosity in
the pellet, unreacted core radius and grain radius, for porosity = 40% (b, d, f and h), for porosity = 20% (c, e, g
and i)
C16 Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114 C17
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
6 Comparison of conversion versus time; analytical 7 Comparison of conversion versus time; analytical
solution by Wen1 (unreacted-core shrinking model) solution by Wen1 (homogeneous model) and present
and present work work
C18 Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
Grain Fg = 3, r0 = 5 mm
Temperature Tb = 1073 K
Fp 1
Fg 3
case the heat generated or consumed by the reaction is T (K) 1073–1373
all transferred across the boundary), the following P (atm) 1
analytical solution is obtained for the temperature r0 (mm) 3·75 x 10–5
rp (mm) 1·283–1·448
profile:5 ε0 66·5%
R V
S _ - DH i D e W Ke (W/m.K) 1·89
T - Ts = S Ke WW_ C As - C A i (43) CPe (kJ/kg.K) 1·49
S fu 0·8
T X ρB (kg/m3) 1800
Figure 9 compares the temperature profile between
MB (kg/kmol) 12
analytical solution and model prediction for a slab-
like pellet. The parameters are given in Table 8. The
temperature profile predicted by the model shows
good agreement with the profile calculated by source term in discretised equations as follows:
analytical solution.
# S U dV = SU DV = S u + S P C CO 2 (49)
CV
where
APPLICATION TO EXPERIMENTAL WORK df G
S u = f G (C -e C CO (50)
CO2 , old)
dC CO o
2
2, old
(C CO2, old)
Carbon gasification reaction with carbon dioxide
df G
The model used for gasification reaction with carbon Sp= e (51)
dC CO o 2
dioxide is: (C CO2, old)
fG = kPCO 2
(45)
1 + k1 PCO + k 2 PCO 2
Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114 C19
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
df G
e dC o is the
CO 2
(C CO2 , old)
C20 Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
show good agreement in regions where the overall rate introduction to computational fluid dynamics, the finite
of reaction is controlled by chemical kinetics or where volume method’, chapter 8, London, Adison Wesley
both chemical kinetics and product layer diffusion are Longman, 1995.
significant. 18. B. KHOSHANDAM: ‘Reduction of cobalt oxide, chromium
oxide, and manganese oxide with methane’, chapter 3,
Unpublished PhD Thesis, Amir-Kabir University of
Technology (Tehran Polytechnic), Tehran, Iran, 2003.
REFERENCES 19. H. Y. SOHN and M. E. WADSWORTH: ‘Rate processes of
1. C. Y. WEN: ‘Noncatalytic heterogeneous solid fluid extractive metallurgy’, New York, Plenum, 1979.
reaction models’, Ind. Eng. Chem., 1968, 60, 34–54. 20. M. HARTMAN and R. W. COUGHLIN: ‘Reaction of sulfur
2. P. A. RAMACHANDRAN and L. K. DORAISWAMY: dioxide with limestone and the influence of pore structure’,
‘Modeling of noncatalytic gas-solid reactions’, AIChE J., Ind. Eng. Chem. Proc. Des. Dev., 1974, 13, 248–253.
1982, 28, 881–900. 21. M. HARTMAN and R. W. COUGHLIN: ‘Reaction of sulfur
3. G. UHDE and U. HOFFMANN: ‘Noncatalytic gas–solid dioxide with limestone and the grain model’, AIChE J.,
reactions: modelling of simultaneous reaction and 1976, 22, 490–498.
formation of surface with a nonisothermal crackling core 22. J. SZEKELY, C. I. LIN and H. Y. SOHN: ‘A structural model
model’, Chem. Eng. Sci., 1997, 52, 1045–1054. for gas-solid reactions with a moving boundary. V An
4. I. A. ABBA and M. A. HASTAOGLU: ‘Modelling of multi experimental study of the reduction of porous nickel-oxide
gas-solid reactions: effect of inert solids’, Trans IChemE, pellets with hydrogen’, Chem. Eng. Sci., 1973, 28,
1997, 75 Part A, 33–41. 1975–1989.
5. J. SZEKELY, J. W. EVANS and H. Y. SOHN: ‘Gas–solid 23. W. F. CHU and A. RAHMEL: ‘The kinetics of reduction of
reactions’, Chapter 4, New York, Academic Press, 1976. chromium oxide by hydrogen’, Met. Trans. B., 1979, 10B,
6. J. SZEKELY and J. W. EVANS: ‘Studies in gas-solid 401407.
reactions: part II. An experimental study of nickel oxide 24. K. J. CANNON and K. J. DENBIGH: ‘Studies on gas-solid
reduction with hydrogen’, Met. Trans., 1971, 2, 1699–1710. reactions. I The oxidation of zinc sulfide’, Chem. Eng. Sci.,
7. J. SZEKELY and C. I. LIN: ‘The reduction of nickel oxide 1957, 6, 145–154.
discs with carbon monoxide’, Met. Trans., 1976, 7B, 493.
8. J. W. EVANS, S. SOHN and C. E. LEON-SUCRE: ‘The
kinetics of nickel oxide reduction by hydrogen,
measurements in a fluidized bed and in a gravimetric
Authors
apparatus’, Met. Trans., 1976, 7B, 55–65. B. Khoshandam has a PhD in chemical engineering in 2004
9. E. C. COSTA and J. M. SMITH: ‘Kinetics of noncatalytic, from Amir-Kabir University (Tehran Polytechnic). He has a
nonisothermal, gas-solid reactions: hydrofluorination of BS degree in chemical engineering – oil industry process
uranium dioxide’, AIChE J., 1971, 17, 947–958. design in 1992 from Iran University of Science and
10. J. B. GIBSON and D. P. HARRISON: ‘The reaction between Technology and MS dgree in chemical engineering in 1997
hydrogen sulfide and spherical pellets of zinc oxide’, I & from Amir-Kabir University. He is a researcher in gas-solid
EC, Proc. Des. Dev., 1980, 19, 231. reactions and a programmer in MATLAB.
11. F. PATISSON, M. G. FRANCOIS and D. ABLITZER: ‘A non-
isothermal, non-equimolar transient kinetic model for gas- R. V. Kumar is a senior lecturer in the Department of
solid reactions’, Chem. Eng. Sci., 1998, 53, 697–708. Materials Science and Metallurgy and a Fellow of Trinity
12. F. LIU and S. K. BHATIA: ‘Solution techniques for Hall at University of Cambridge, UK. He obtained hid PhD
transport problems involving steep concentration from McMaster University in Canada. His research
gradients: application to noncatalytic fluid solid reactions’, interests include thermodynamics and kinetics of
Comput. Chem. Eng., 2001, 25, 1159–1168. metallurgical and materials processing, metal refining and
13. N. WAKAO and J. M. SMITH: ‘Diffusion in catalyst pellets’, recycling, electrochemistry, solid state ionic sensors for
Chem. Eng. Sci., 1962, 17, 825–834. process and pollution control, processing of sensors and
14. E. A. MASON, A. P. MALINAUSKAS and R. B. EVANS: actuators, and sustainable technologies.
‘Flow and diffusion of gases in porous media’, J. Chem.
Esmail Jamshidi is Professor of the Department of Chemical
Phys., 1967, 46, 3199–3216.
Engineering, Amir-Kabir University (Tehran Polytecgnic).
15. R. B. BIRD, W. E. STEWART and E. N. LIGHTFOOT:
He has a BS degree in chemical and petroleum engineering
‘Transport phenomena’, chapter 16, New York, Wiley,
fron Tehran University in 1964, MS and PhD degree in
1960.
chemical engineering and materials science from Wayne
16. W. E. RANZ and W. R. MARSHALL: ‘Evaporation from
State University in 1971 and 1973 respectively. His research
drops’, Chem. Eng. Prog., 1952, 48, 141–146, 173–180.
interests are methane reactions wit inorganic chemicals.
17. H. K. VERSTEEG and W. MALALASEKERA: ‘An
Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114 C21
Khoshandam et al. Simulation of non-catalytic gas–solid reactions
APPENDIX – NOTATION
A, C Gaseous reactant and product, respectively r Radial position in the grain (m)
Ag, Ap External surface area of individual grain and rc Radial position of the reaction front in grain (m)
pellet, respectively (m2) rcp Radial position of the reaction front in
B, D Solid reactant and product, respectively analytical solution (m)
b, c, d Stoichiometric coefficients rg Radius of the grain (m)
CB0 Initial concentration of solid reactant rp Pellet radius for spherical and cylindrical pellets
(kmol m–3) and half-thickness for slab-like pellets (m)
CA Gaseous reactant concentration in the pellet S Average value of source S over the control
(kmol m–3) volume
CAb, CAs Gaseous reactant concentration in the bulk of SΦ Source term in Equation (31)
gas and on the external surface of pellet, Su, Sp Constant coefficients in the linear source model,
respectively (kmol m–3) Equation (32)
C CO2 Concentration of carbon dioxide in the bulk of T Temperature (K)
the gas phase t Time (s)
C CO , old Concentration of carbon dioxide in the bulk of
2 u∞ Velocity of gas stream (m s–1)
the gas phase in the previous time step Vg, Vp Volume of individual grain and pellet,
CPe Effective specific heat capacity of the pellet respectively (m3)
(J kmol–1 K–1) X Overall solid conversion for the pellet
CPf Specific heat capacity of gas stream x Local conversion in the pellet
(J kmol–1 K–1) Z Volume of solid product from unit volume of
CPs, CPg Specific heat capacity of solid and gas, solid reactant
respectively (J kmol–1 K–1) z Position in the pellet, radial position in spherical
CV Control volume and cylindrical pellets and axial position in
De Effective diffusion coefficient of gaseous slab-like pellets
reactant through the pellet (m2 s–1)
DAp Diffusivity of gaseous reactant A in the product
GREEK LETTERS
layer (m2 s–1)
Γ Diffusion coefficient of property Φ in Equation (31)
DAK, DAM Knudsen and molecular diffusivity of gaseous
∆H Heat of reaction (J kmol–1)
reactant A through the pellet, respectively
ε Porosity of the pellet
(m2 s–1)
fu Emissivity of the pellet
dp Diameter of pellet (m)
θ Dimensionless time
Ea Activation energy (J kmol–1)
µf Viscosity of gas stream (kg m–1 s–1)
Fp, Fg Pellet and grain shape factor, respectively
ξc Dimensionless radius defined by Equation (41)
fG Rate of surface reaction (kmol m–2 s–1)
ρ Density (kg m–3)
hc Convective heat transfer coefficient (W m–2 K–1)
ρf Density of gas stream (kg m–3)
Ke Effective thermal conductivity of the pellet
σ Stefan-Boltzmann constant 5·67 10–8 (W m–2 K–4)
(W m–1 K–1) t
v Generalised gas–solid reaction modulus defined
Kf Thermal conductivity of gas stream (W m–1 K–1)
by Equation (46)
Ks, Kg Thermal conductivity of solid and gas,
τ Tortuosity coefficient of the pellet
respectively (W m–1 K–1)
Φ A scalar property in Equation (31)
k Reaction rate constant (m3n-3m-2 kmol1-m-n s–1)
ΦP Property Φ at a general nodal point P
kv Reaction rate constant based on volume
ϕ Thiele modulus
(m3(m+n-1) kmol1-m-n s–1)
kc Convective mass transfer coefficient (m s–1)
k0 A parameter defined in Equation (25) DIMENSIONLESS NUMBERS
k1 A coefficient in Equations (21) and (45) Nu Nusselt number = hc dp/Kf
k2 A coefficient in Equation (45) Pr Prandtl number = CPf µf/Kf
k′ Frequency factor (kmol1-m-n s–1 m3n-3m-2) Re Reynolds number = ρf u∞ dp/µf
M Molecular weight (kg kmol–1) Sc Schmidt number = µf/ρf DAM
n, m Exponent of the reaction rate dependence on Sh Sherwood number = kc dp/DAM
the reactant concentrations
nd Number of solid grains per unit volume of SUBSCRIPTS
porous solid (m–3) 0 Initial conditions
P Total pressure b Bulk of gas flow
PCO , PCO Partial pressures of carbon dioxide and
2 i Reaction front condition
carbon monoxide s External surface of the pellet
R Ideal gas constant (J mol–1 K–1) w Inner walls of the reactor
C22 Mineral Processing and Extractive Metallurgy (Trans. Inst. Min. Metall. C) March 2005 Vol. 114