Chemrcni Engmeenng Scaence Vol 35, pp 1CL- 16 Pergamon Press Ltd , 1980, Pnnted m Great Bntaln
2
EFFECTIVE
DIFFUSIVITIES REACTIVE
D.
Ryan,
R.G.
FOR CATALYST CONDITIONS
Carbonell
and
PEZLETS
S.
UNDER
Whitaker
Department of Chemical Engineerzng University of California Davis, Californza 95616 U.S.A.
ABSTRACT A theory is developed that allows the calculatron of the components of the effective diffusivity tensor under reaction conditions In spatially periodic porous media. Under normal conditions, it can be shown that the effective diffusivity should be independent of the rate of the chemical reaction. Preliminary calculations are provided illustratlng the effect of the particle void fraction on the effective diffusivlty.
KEYWORDS Effective diffusivities; porous me&a.
catalyst
pellets,
reaction
conditions;
spatially
periodic
INTRODUCTION lateness of using effective Many investigators have raised the questlon of the appro y&ve conditions m the design diffusivlties for catalyst pellets measured under non-r *ed Naruse (1974) used asimRecently, Wakao (1974) and Wa 3 of packed bed reactors. ple grid of macro and micro pores to show that effective diffuslvitles under passive conditions would be larger than those under reaction conditions, but that this difference would decrease conslderably in the presence of a small percentage of dead-end pores. These results are in agreement with earlier studzes by Wakao, Kimura and Shibata (1969) who found experimentally that effective diffusivitles under non-reactive conditions were larger by a factor of 3 or 4 than the reactive effective diffusivities in
the
para-ortho
H2
later results of Toei catalyst. Balder and fective diffusivities cal.
conversion
reaction.
and co-workers Petersen (1968) under reactive
This
also
(1973) on the on the othet and non-reactive
seems
to
hydrogenation found hand, conditions
be
in
agreement
with
the
of ethylene on a Ni experimentally that efare essentially identi-
used the Foster and Butt (1966) convergent-divergent Similarly, Steisel and Butt (1967) pore model and the pore size distribution reported by Otanl and Smith (1966) to show that the reactive and non-reactive effective diffusivitles for the oxidation of CO there seems to be some conflicting information as to came out to be the same. Thus, the effect of reaction rate on effective diffusivitles. we present the results of an analysis of combined molecular diffusion In this paper, This model offers some with chemical reaction in a spatially periodic porous medium. in catalyst pellets [Foster and distinct advantages over previous models of the pores Johnson and Stewart (1965): Wakao and Smith <1962), Brown and Haynes Butt (1966); Since It can Haynes and Manogue (1969); Youngquist (197O)l. (1969, 1971:; Brown, it yields all of the components of the effective diffusihandle anisotropic systems, vity tensor, and can be used to study the effect of packing and particle shape on the In the sections that follow we present the theoretical developeffective diffuslvity. and a comparison with experimental ment, the results of calculations on a model system, data on effective diffusivities for unconsolidated porous media, Theoretical
Development 10
Effectivedlffumvlhes for catalyst pellets under reactiveconditions
A-2
Consxder
the
particle
catalyst
to
Fzgure medxum is the fluid phase being transported in the fluid phase
be
1
while the o by molecular is governed
a
porous
medium
AveragIng
as
shown
V rn
volume
phase 1s the solid diffusion alone so by the equation,
a
in
11
Fig.
The
1.
phase
a
porous
phase. Withln that the local
a solute the pores, or point concentration
o=w2c
1s
(1)
where we have assumed the molecular diffusivity to a steady-state At the fluid-solid em. is taking place Jo that the boundary condition -DsEc=kc
on
a unit normal !z sents the fluid-solid of the intrlnsxc rate to the solid phase.
restrxct chemical
ourselves reaction
(2)
ou
pointing
with
We are interested txon in the fluid
A
is a constant and we interface a first order for Eq. (1) becomes,
from
the
fluid
into
the
solid
interfacial area. The reaction rate constant and an equilxbrium constant
in obtaining an phase [Wbxtaker
equation (1970)],
for
the
phase
constant for the
intrinsic
phase
and
Aoo
repre-
k is the product adsorption of solute
average
concentra-
(3)
where
V
(x
particles concentration plying the
is as
the
volume
shown
in
of
Fig.
locally within spatial averaging
= v-cc> +
the 1.
CL This
phase is
within
an
averaging
a measure
of
the
the particle. We theorem FWhitaker
can obtain (1970)],
volume
average an
V
containing
interstitial
equation
for
many
solute ccBa
by
ap-
1
(4)
dV
(5)
where c
12
A-2
1s
the
phase-average
concentrations with
c
=
concentration 01
cc> =
and
xc>
and
are
Aoo
related
is
by
the
the
interfacial
void
fraction
area
V.
within
The
E,
a
ECC>
(6)
Vu/V_
Takxng the phase tion Eq. (2) one
average quickly
of Eq. arrives
(1) at
and the
making result,
~v-
0 -
use
of
Eq.
(4)
and
the
boundary
condi-
-b;[cdA
(7)
CUJ By
writing
the c
and
makxng
point
concentration
c
in
terms
of
use
(9)
of
the
a
Note
that
ferential by taking substituting
V
if
and
a
deviation
z
[Gray
(1975)],
Oc+ ;
=
Eq.
(8) (6),
we
can
transform
Eq. ka - 2 D
In Eq. pellet,
Cc>u
quantity
=
Am/v
we
is
av
equal
to
the
(7)
to
the
form
CL
surface
(9)
area
per
unit
volume
of
catalyst
.
could
(10) express
equation for the the point equation Eq. (8),
z
In
terms
of
interstitial for c, Eq.
<,>a,
Eq.
concentration (l), and the
(9)
would
~. boundary
yield
a
This can be condition,
governing
dxf-
accomplished Eq. (2), and
(11) -Dn-VT -1 If the
-
field The
k"c =
ko
+
were available, "c solution will
Dn*_
Vu
on
(12)
AW
Eqs. (11) and (12) undergo significant
would result changes over
in a description of distances Y on the a order of the radius of a pore between particles, while average concentration varies over distances L on the order of the catalyst particle radius, Y/L << 1. From an order of magnitude estimate of the terms in the boundary condition Eq. (12) it is quickly concluded that the ratio, (13) for all normal reaction rates encountered in practice. Similarly, it ing the theory of Green's functions [Arfken <1970)] that the solution be closely approximated by the solution to the homogeneous problem,
v%= whenever y/L z simplifies -U In
order
to
where
L
and
-
obtain
. s
uscan
(14)
no 0;
Z=f
shown (11)
0
<< 1. to,
c
can be to Eq.
Using
result
Eq.
=
k~
a
solution
lv
..?-
are
the
a
+
s
a vector
to
Eq.
(13)
on
A
(14).
we
in
Eq.
<12),
the
boundary
condition
for
(15)
aa represent
the
function
E
as
a (16) and
a
scalar
function
of
position.
Substituting
Eq.
(16)
13
Effectivedlffusnrrnesfor catalyst pelletsunder reactivecon&uons
A-2
Into Eqs. (14) and (15) we can develop boundary conditions at the fluid-solid reaction rate and is governed by,
equations interphase.
for
both The g
r and field
s with appropriate does not depend on
the
(17)
- n-Vf
=
Y-
The s shown
field to be
is
on
reaction
v2s = -
n
(18)
Aoo
rate
dependent
and
its
governing
differential
equation
may
be
(19)
0
=
n-Vs _I
k/D
on
(20)
Aoo
f and s equations as given are still formidable, since the The solutions to both the However, if we 1 is extremely complex. geometry of a porous medium as shown in Fig. consider the special case of a spatially periodic porous medium, as described in detail one can show that the f and s fields should be spatially periodic. by Brenner <1979), 2 we show a typical two dimensional spatially periodic array of particles. In Fig.
Two dlmenslonal Frgure 2 rlodlc porous medrum with Ice vectors Rland IL.2 vectors
The and
fl
entire as z2
array shown.
spatially unit cell
may be generated from a The spatial periodicity
pelatt-
single of
f
unit cell and s
with lattice implies that,
f (2)
= f(f
+ _el)
1 =
1,2
(21)
s(5)
=
+ _e,)
i =
1,2
(22)
S(f
One can easily extend this idea to a threeIS a spatial position vector. where r The spatially periodic porous medium does not have to dimensi%al array of particles. Since the and the unit cell can contain more than one type of particle. be isotropic, (17) and (19) need only be solved within a unit cell, f and s fields are periodic, Eqs. znd this greatly simplifies the computational effort required to obtain a solution for z. Once Eq. tam,
the (9).
f functions the governizg
use
dzffusivity
have for
,eff:~~~c>a - ka/c>o
O=D where
and s equation
has
been
tensor,
made
of
defined
Eq. by,
(13).
been the
+
one can substitute Eq. determined, intrinsic phase average concentration
DE
~-Vo _-
In
Eq.
(23)
(16) to
into ob-
(23) the
quantity
,Deff
is
the
effective
14
Knwtzcsand
sDeff -= where
U .z
is
the
vector
unit
that
zeff
5
is
J A
A-2
TJ
(24)
?z
tensor
and
T r
r =a!--- 1 vo v
Note
D Et&+
E
Cataiysrs
is
the
tortuosity
tensor
fWhitaker
(1967)]
(25)
n f dA _CLCS
is
independent
defined
of
reaction
rate
since
f
is
independent
of
k.
The
by,
(26)
and it appears in a convective term in Eq. (23). The vector 6 depends on rate through the parameter f3 = kY/D. This parameter appears Then Eq. (20) mensionless using a mean pore radius, Y as the characteristic length. It ficult to determine from order of magnitude estimates for real systems that -4
normally less than 10 , and that as a essentially equal to zero. This makes and results in, 0 as the section
=
CL
gef f :_o~
governing equation that follows, we
-
for the consider
isotropic two dimensional the results to experimental
Results
and
As a simple sional unit
spatially cell shown
with
s
and term
5 should be very small, x;Eq. (23) insignificant
(27)
kava
versely compare
Comparison
result both the convective
average interstitial solute some preliminary calculations spatially periodic observations.
Experimental
periodic in Fig.
r eat t ion is made diis not difB << 1,
model
of
concentration. In the of for a transQeff a catalyst particle, and
Data
model of the The cell 3.
catalyst pellet, we consider is identically square with
Figure 3 Two dxmenslonal spatially rlodlc model for a catalyst pellet blocks are cubes of length IL The of the unzt cell have a length of The void fractxon E = 1 - ab/R2
peAll srdes
I
the two dimenside length e,
A-2
1s
Effective&ffumvltles for catalystpelletsunder reactivecondltlons
The value of the void fracand gives rise to transversely isotropic porous medium. Equation (17), subject to can be varied by changing the values of a and b. tion E and the spatial periodicity constraint Eq. (21). was boundary condition Eq. (181, and f The problem was namely, fx solved for both components of the vector ,fa Ysolved numerically using a Gauss-Seidel successive over-relaxation scheme [Roache The relaxaAx = Ay = l/60. The unit cell was divided into steps of size (197611. and the calculations took approximately 5000 Ittlon parameter used was equal to 1.4, were calculated directly by the The components of the tortuosity tensor 5 erations. area Integral in Eq. (25). Since the system 1s transversely isotropic then =-C and T =-c =O. This me&s there is only one independent non--zero comT YY Yx xY ponent of the effective diffuslvity tensor, and It is given by D eff -
D
according In
Fig.
to 4 we
=
[l +
E
Eq.
(28)
Txx3
(24).
show
theoretical
values
Deff /U
of
for
various
values
of
E
for
the
unit
0 SOI 1 crumbs
05
A Pumice -Talc . Kaolxn ce1rte
04
r\
1
2 w=-
I
l
I
rVermrculltc vM1.X i
a 011 02
01
I
I
03
04
LIIIf 05nbO708
10
E
Comparison of theoretlcal Figure 4 with expertpredlctlons Eq (281, mental data of Currle [ '601 on the drffuslon of hydrogen In air through beds of unconsolidated sollds (After SatterEffect of the porosity field 1'701 ) E: on the ratlo of the effective dlffuslvlty to the molecular dlffuslvlty cell of Fig. 3. These are compared to the experimental results of Currie (1960) for diffusion in beds of various unconsolidated porous media as presented by Satterfield (1970). When a = b, the agreement between theory and experiment 1s excellent, except for materials such as vermiculite and mica that exhibit a more layered structure. When the ratio a/b = 3, we find that the slope of the theory line is much steeper as the experimental results for these materials seem to indicate,
NOMENCLATURE a A
Surface
V
cc0
C
CC>
z u
zeff
Fluid-solid Point Phase
cc> a
area
per
unit
volume
interfacial
of
catalyst
area
concentration average concentration
Intrinsic
phase
Deviation Molecular Effective
of c from diffusivity diffusivity
average
concentration
XC>
a
tensor
Kmetzcs and Catalysm
16
A-2
Vector function of position Reaction rate constant Lattice vector Length of cube in two-dxmensional array Characteristic catalyst pellet dimension Unit normal from the fluid to solid on
AaB
Characteristx pore dimension Spatial position vector Scalar function of position Unit tensor Volume of the averagxng volume phase with V Volume of a Greek
Symbols
a 5 : F r r
Fluid phase Solxd phase Dimensionless reaction Rate dependent vector Voxd fraction Tortuosity tensor
rate
parameter
Methods
for
REFERENCES Arfken .A,;.
(1970).
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Physicist,
2nd
Ed.,
Academic
Press,
New
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