rmin, respectively. The region of validity of Eq. (24) is quite narrow (see Fig. 2). However, if Plim it were 10-100 atm, the region of validity of Eq. (24) would widen considerably. The gas pressure in the pores may be limited by particle deformation (for softening coals), condensation (tar), or to the value at which the volatfles exist in gas phase at near solid densities (3000 atm). Hence, the limiting pressure may, depending upon the physi-
where rp* = 16# G V/(3PG).
(26)
Similarly, the transition from continuum diffusion to viscous convection is determined by equating Eqs. (14) and (17) for D = De. Therefore, Transition, Continuum/Viscous: rp = (37r/64)l/Zrp *.
(27)
Comparison of Eqs. (25) and (27) indicates that continuum diffusion limits the gas velocity
SPECIES TRANSPORT IN COAL PYROLYSIS
187
only in a very narrow range of pore radii from 0.15rp* to 0.28rp* and, for all practical purposes, may be disregarded from further consideration. The fluid mechanical process then undergoes transition directly from Knudsen diffusion to viscous convection. This transition radius is obtained by equating Eqs. (14) and (17) for D = DEN. Therefore, Transition, Knudsen/Viscous: rp = rp*.
(28)
The transition radius r* is given by Eq. (26) and may be evaluated by utilizing the Knudsen solution for PG(rp). Hence, Eqs. (20) and (26) yield
where all pore trees whose trunk radius is less than rt* are limited entirely by Knudsen diffusion and all r t > rt* are limited entirely by convection. This conclusion is based solely on an assessment of viscous convection, and the limiting regimes are illustrated in Fig. 3. The role of volatile drag in the convection solution for rt >>rt* is now addressed. The boundary between viscous drag and volatile drag is denoted r** and is determined by equating Eqs. (17) and (18). Therefore, Transition, Viscous/Volatile: rp = r**,
where rp* _ exp [ 32#GV2
9klt2pref
rmtn
11 .
(n)l/2Ko , r **=
The argument of the exponent will vary over several orders of magnitude and rp* will vary from rmi n to rma x while the argument of the exponent varies from 1 to 10. Thus, for all practical purposes, the entke pore tree will switch from Knudsen control to viscous control when the argument of the exponent is of order 3. The transition radius rt* is defined by rt* =
Ko
10o A
=L v Z a.. I-Ukl W
az i-
< eel
I
~,== rt = r* I ~ I ~ 10~ . I
~
r t -20rt*.
Every pore tree whose trunk radius is less than r** contains only pores whose radius rp is less than r**. Thus, in the size range rt* < r t < r**, viscous convection limits the fluid transport in the entire pore tree. When r t > r**, the pore tree contains both rp > r** and rp < r**. The volatile drag solution (rp > r**) must match the viscous drag solution (rp < r**) at rp = r**. This solution is called the General convection solution and is applicable for all r t > r**. The
I
I
GENERAL CONVECTION • VOLATILE DRAG: rp ~ r** " VISCOUSDRAG : r p < r * " ~CONDUCTION LIMITED _
rt" rt
~~
~j(
ALL VISCOUS CONVECr'ON
,-
~
10
102
(30)
~~i=m~i=t ~
=30OOo~.
103
104
k -- INTRINSICPYROLYSISPATE (=-1) Fig. 3. F l u i d m e c h a n i c a l r e g i m e s .
105
188
GIRARD A. SIMONS
three fluid mechanical regimes are summarized by rmi n ~ < r t ~ < r t * :
All Knudsen Diffusion,
rt* ~
All viscous Convection,
r** ~
General Convection.
The range of applicability of these three regimes is illustrated in Fig. 3. Note that all three fluid processes may dominate the mass transport in some range of trunk radius and pyrolysis rate (k). However, the heat conduction through the coal will be shown to prevent the pyrolysis rate from ever achieving the level necessary to allow volatile drag to dominate the convection solution. At time t after a heat source is supplied, thermal conduction will transport the thermal energy a distance 6 from the surface of the coal particle. The thermal depth 6 is given by 8 = (2at) z/2, where t~ is the thermal diffusivity (0.02 cm2/s for coal). The pyrolysis chemistry is occurring in an isothermal environment if and only if the thermal depth is greater than a characteristic tree height (5 > It) in a time shorter than the chemical time (t < l/k). This criterion is expressed as
1/2 0113 r t < r*** =
is controlled by Knudsen diffusion and that where the entire tree is controlled by viscous convection. The Knudsen solution was obtained in Section 4. The value of r t corresponding to Pmax = Plimit is determined from Eqs. (21) and (5). By normalizing this value o f r t by rt*,
rt(Plimit) = ( 2Plimitrmin~112, rt*
\
6. TREESCONTROLLEDBY VISCOUS CONVECTION For those pore trees whose trunk radii are of sufficient size that the mass transport in the entire tree is limited by viscous convection, the mean flow velocity is given by Eqs. (17) and (4): =
rP 3
dp G
8lda 6
drp
drp
Ko V \ lr/ae /
where riv
8#6klt2pref ln(rp/rjv) rp 3
,
(32)
represents the value of rp where
pG(rp, rt) ~ Pnmit- Integration of Eq. (32) yields F41aGklt2pr'~ (2 ln(rp/ryv) + 1} PG(rp, rt) = L rp2
r * * * _ 01__/_ a (2otPre___._~ f y/2 r*--~
(31)
Eliminating ~ between Eq. (31) and the transport equation, Eq. (11), yields PG ---
and establishes an upper limit on the values of k and r t that are of practical importance. The ratio oft*** to r** becomes
]
it is shown in Figs. 2 and 3 that the limiting pressure of 3000 atm (or less) is always attained in the Knudsen regime. Hence, the viscous regime will always correspond to conditions under which the gas pressure attains Plimit in the leaves of the tree. The viscous solution, subject to this constraint, is developed below.
dpG
Ko
3PGV
~ 1
and demonstrates that the general convection solution is not applicable due to the finite thermal conductivity of coal. Analysis of the volatile mass flux during pyrolysis has thus been reduced to two relatively simple idealizations: the case where the entire tree
+A21 x/2,
(33)
where A 2 is an arbitrary constant of integration to be determined by the boundary condition on the gas pressure at rp -- rt.
189
SPECIES TRANSPORT IN COAL PYROLYSIS Just as in the Knudsen controlled regime, the internal pressure is independent of the background environment if the pore radius is much smaller than the trunk radius. Thus, for rp ,~ rt,
which is Eq. (11) revised to allow ~ = 0 at rp = rj. The mass flux of a perfect gas becomes pG~rrr p 2
-
8kltPrefrp2
~2
ln(rv/ri)"
PG(rp, rt) ~ (21t/rp)(kllGPref) 112 × [2 ln(rp/rjv ) + 1] 1/2.
(34)
Comparison of Eqs. (20) and (34) demonstrates that the solutions for the gas pressure in the Knudsen and viscous regimes are nearly compatible at the transition radius rt*. Knudsen PG(rt*)
3 [1 + ln(rp/rjK)]
Viscous pG(rt* )
411 + 2 ln(rp/rjv)] x/2
which, when evaluated at rp = r t, represents the total volatile flux per pore tree,)l;/t:
)flit =
Mv =
Thus, the e½act solutions are consistent with the approximate analysis of the fluid mechanical regimes. The pore radius at which pG(rp, rt) is equal to Puraa is denoted riv and is obtained from Eq. (34): 21t =
~2
ln(rt/5)"
The total volatile flux per particle, 3~/v, is obtained from the integral o f M t over all r t. Hence,
0.75 -- 1.5.
r/v(rt)
8kPrefltrt 2
rfrmnax /~tg(rt)41ra 2 dr t in
(37)
where ~(rt)dr t represents the number of pores per unit area in size range rt to rt + drt [3, 6],
g(rt) = O/(27r~rt3), a is the particle radius, and = ln(rra.x/rrain).
(klAGPref) 112 .
(35)
Plim it
The largest value of rp is related to the particle radius by [3, 6],
The solution for pG(rp, rt) is now rewritten as
rra ax = 201/3a/(3Ko),
PG(rp, rt) = Plirait [ "_LL.*] [2 ln(rp/rjv )
+
1] x/2
\rp /
and rmin is the smallest value Ofrp [6] (36)
and demonstrates the same behavior with rp as the Knudsen solution. However, the dependence of pG(rp, rt) on the trunk radius and the pyrolysis rate is different in the Knudsen and viscous regimes. 7. FLUID MECHANICAL RETARDATION OF THE DEVOLATILIZATION RATE The mean velocity of the volatiles in the pore tree is given by
=
kltPref PG
main = 20/(OPsSp), where Sp is the specific internal surface area (typically several hundred mg-/g). Normalizing ~/v to the total mass of the volatiles, M v = ~ ~raaps(O f -- 0),
the total volatile mass flux becomes
My_ Mv
3 k K 0 rfrmn ax 2a/30x/a ln(rt/rj) dr t.
(38)
in
ln(rp/ri) ,
It is readily shown that when rj =/'rain, i.e., when
190
GIRARD A. SIMONS
PG ~ Plirait for all (rp, rt), Eq. (38) yields
M v / M v = k,
(39)
which is the basic definition of the pyrolysis rate k introduced in Eq. (9). The role of Plirait is now obvious. Whenever PG ~ Plimit, ff is zero in those pores and the volatile mass flux is reduced. This is readily illustrated by Eq. (38): ~,lv/M v is less than k for all ri i> main. Integration of Eq. (38) requires specification of r~ for all rt. If PG < Plimit for all (rp, rt), then rs = rmin and the entire pore tree is outgasing without fluid mechanical retardation. Once Plimit is exceeded, r/assumes the values of rSk and rjv in the Knudsen and viscous regimes, respectively. However, if PG ~ Plimit in the trunk of the tree, ~ = 0 everywhere and rj is set equal to r t so that 3~/t is zero. Similarly, if r t > rt***, thermal conduction within the particle limits ~/t and r~ is set equal to r t. In this manner, values of ~lv/Mv are determined as functions of three parameters: intrinsic pyrolysis rate, particle diameter, and Plimit" Figure 4 illustrates the fluid mechanical retardation of the devolatilization rate (3;/v/Mv). Increasing values of Pltmit result in the increasing ability of the fluid mechanics to keep up with the intrinsic pyrolysis rate. Bituminous coals are known to exhibit reduced tar yields at background pressures greater than 1-10 atm. This may be ex1000
I l ilillt
I
plained on the basis of tar condensation pressures of the order of 1-10 atm [8]. In addition, bituminous coals do deform and may not be structurally capable of supporting internal pressures greater than 10 atm. If PUmit of 1-10 arm is associated with bituminous coals, then Fig. 4 predicts that the maximum observed devolatilization rate would be I 0 - I 0 0 ( s - l ) . This is consistent with observation [5, 9]. If Pllmit = 3000 atm is associated with lignite (no deformation or tar condensation), then Fig. 4 predicts that the devolatilization rate is nearly equal to the intrinsic pyrolysis rate. Increased ambient pressure would not influence the devolatilization of a lignite, whereas it would strongly influence that of a bituminous coal. This is consistent with observation [5]. The effect of particle size on the devolatilization rate is illustrated in Fig. 5. For small values of Plimit(<30 arm), the devolatilization rate is strongly dependent on particle size, whereas this dependence does not occur for Pumit = 3000 atm. This implies that the devolatilization of a lignite is not particle size dependent, whereas that of a bituminous coal is. An interesting feature illustrated in Fig. 5 is that the devolatilization rate is independent of the thermal conductivity of the particle, even for 1 mm particles. This is due to the low value of Plimit- The fluid transport terminates the volatile mass flux before thermal conduction
I I Ililii I
I I III1~1~)00111111~
n-
N 3 s~
--
.>,
1 - ' ~ / ~ l 1iIIII1 2 0 I 0 I K Illlld 1 10 100
I I I IIIIII 114~. K) , I III~IIKI~I 103 104
k - INTRINSIC PYROLYSIS RATE (=--1)
Fig. 4. Fluid mechanical retardation of the devolatilization rate.
SPECIES TRANSPORT IN COAL PYROLYSIS 103
I
< Z 102 _o t< N .J
__--
< ..>.
I IIIIII
I
I
Plimit = 3 atm O~=0.02cm2/s
I
to
191 I IIIIII
I
I
co
I IIIIll
/
/ /
I
I
I
IIIIH
10/z DIAMETER
~
--
S ~ D I. A M ~ E T E R
_--
10
I
/
~ , ,,n,.,
..~?~,ooK)..~.,.%ooK), , ,,,,,,., , .,,,,,,i
10
102
.(1.~) , .,,..,,
103
104
k - INTRINSIC PYROLYSISRATE (s-1) Fig. 5. Effect of particle size on the devolatilization rate.
1 0 a S- 1 . If the particle heating rate were in excess of 10~ S- 1 , any devolatilization rate observed to proceed slower than 10 a s- 1 would suggest transport limitations. Predictions corresponding to these conditions are illustrated in Fig. 7. The devolatilization rate is directly proportional to Plirait and inversely proportional to particle diameter. These calculations suggest that rate measurements at these conditions could be used to test empirically the present theory. The fluid mechanical retardation occurs because a large fraction of the volatiles stagnate in the pores at pressure Plimit- Since (.,flv/Mv)k is the
limits k. As Plirait is increased, fluid transport increases and thermal conduction can become rate limiting. An example of this limit is illustrated in Fig. 6 for Plimi t = 300 atm and 1 mm particles. The examples illustrated in Figs. 5 and 6 suggest that the particle size dependence of the transport limited devolatilization rate may be used to scrutinize empirically the pore structure, pore evolution, and volatile transport models. Volatile transport will limit the devolatilization rate if the heating rate and the intrinsic pyrolysis rate are sufficiently large. At temperatures in the range of 1700-2000K, k may be in excess of
A
103
I
I IIIIII
I
I
I IIIIHI
I
I IIIIII
Plimit = 300 atm lmm DIAMETERPARTICLE
I
I
~-/ / ~ !oo
I IIIli:l:
"~ ---------
/// Z
102
N
.3
_
,,.o.o....,. I
I Illllll
I
10.
I |llllll
102
I
I II||lll
I
103
i I Illlll
104
k - INTRINSICPYROLYSISRATE ($--1) Fig. 6. Influence of thermal conductivity on the devolafilization rate.
192
GIRARD A. SIMONS 103
Section 4 and suggests vast potential for secondary chemistry. 8. CONCLUSIONS
i u.i <
cc
:p O I<
10 2
N_
,,J I< .J 0 w e~
10
I
ff ,IE
1 10
10 2
103
PARTICLE DIAMETER (#)
Fig. 7. Prediction of transport limited devolatilization rate.
A model has been developed to describe volatile transport during pyrolysis. The rate of volatile release is described parametrically in terms of a single intrinsic pyrolysis rate k. The pore evolution model of Part I [3] prescribes the origin of the volatfles on the walls of every pore in every tree in the particle. The species are transported through the pore tree by diffusion and/or convection. Within reasonable limits of approximation, small trees are controlled primarily by Knudsen diffusion and large trees by viscous convection. The largest pressures occur in the smallest branches of the largest trees. Internal pressures are limited by several phenomena, and the limiting internal pressure is represented parametrically by Plimit- Decreasing values of Plirait result in increased fluid mechanical retardation of the volatile flux. Values of Plimit
fraction of volatiles that escape the pores, 1 must represent the fraction of the volatiles that exist at pressure Plimlt. Figure 8 illustrates that a very large fraction of the volatiles experience pressures of 300-3000 atm. Indirect observation of this prediction was discussed in
Mv/kMv
= -
I
I tlllll
I
I I Illlll
approximately 1 - 1 0
I
I
I IIIlill
I
I III1~
_
-
100~ D I A M E T E R PARTICLES Ol= 0.02 cm2/s
1
/ -
of
1
3 ate....... ~ "
o.,yS -
-10-2,,
I lllllilJ
atm
correspond to bituminous coals. The predicted devolatilization rates for these values of Plimit are sensitive to particle size and background pressure but will not exceed 10-100 s- 1 . Such predictions are consistent with observations for bituminous coals [5, 9].
/ (1000K) 11200K1 11400K1 11800K I Iaaatlii I IIl[Zlal I IIIIII 10 102 103 104
k - INTRINSIC PYROLYSIS RATE (s-1)
Fig. 8. Fraction o f gas experiencing pressure p during pyrolysis.
SPECIES TRANSPORT IN COAL PYROLYSIS Values of Plimit of the order of 1000 atm correspond to 1ignites. At these high pressures, no particle size or background pressure dependence is predicted. This is consistent with observation [5]. These high pressures are shown to be in reasonable agreement with the pressures suggested by Suuberg et al. [7] and clearly indicate vast potential for secondary chemistry, It is noted that the present study has concentrated only on the role of fluid transport, treats the intrinsic pyrolysis rate and the limiting pressure parametrically, and in no way represents a complete devolatilization model. Mechanistic chemical models (or definitive empirical models) for k and Plirait must be developed and coupled to the fluid transport model. The model for k must include the finite thermal conductivity and the finite external heating rate. While this work does not describe such a complete model, it does demonstrate that fluid transport plays a dominant role in devolatilization and that devolatflization models must include the coupled effects of chemistry and fluid transport.
193 Pref p~. rp mmin rmax rt r*
r** r*** rj rjK rjv R sp t T V Y
reference pressure-Eq. (12) background pressure radius of pore radius of smallest pore radius of largest pore radius of the pore that represents the trunk of a tree pore radius corresponding to transition from Knudsen diffusion to viscous convection pore radius corresponding to transition from viscous to volatile drag pore radius corresponding to the onset of conduction limitations. radius of pore for which U(rp, rt) = 0 value ofrj in Kundsen regime value ofri in viscous regime gas constant specific internal surface area (area/mass) time temperature bulk velocity of volatiles mean thermal speed of a molecule skewed coordinate in pore tree
NOMENCLATURE a
radius of porous particle speed of sound in gas diffusion coefficient D Knudsen value of D DKN continuum value of D Dc pore distribution function per sample area intrinsic pyrolysis rate k constant ~ ratio of pore length to diamKo eter ~- 5 length of pore of radius rp length of the pore that represents the it trunk of a tree pore roughness factor (3/2) m rate of mass removal from walls of pores rnw volatile flux per pore tree volatile flux per particle Mv total mass of volatiles Mv nfy) number of pores of radius rp at location y in pore tree gas pressure at (rp, rt) PG Plim it upper limit on PG in the pore P m ilx value of PG at (rmin, rt)
Greek Symbols
t~
thermal diffusivity In (rmax/rmin) 0 porosity Of final porosity after pyrolysis /zG gas viscosity PG gas density Ps density of nonporous material amax material yield stress
Work supported by U.S. Department o f Energy, Pittsburgh Energy Technology Center, under con tract DE-A C22-80PC-30293. REFERENCES 1. Russel, W. B., Saville, D. A., and Greene, M. I., AIChE
J., 25:65 (1979). 2. Gavalas, G. R., and Wilks, K. A., AIChE J. 26:201
(1980). 3. Simons, G. A., Combust. Flame, 53:83 (1983). 4. Simons, G. A., Comb. $ci. Tech. 19:227 (1979).
194
G I R A R D A. SIMONS
5. Anthony, D. B,, and Howard, J. B., AIChE J. 22:625 (1976). 6. Simons, G. A., and Finson, M. L., Comb. Scl Tech. 19:217 (1979). 7. Suuberg, E. M., Peters, W. A., and Howard, J. B., i & EC Proc. Des. Dev. 17:37 (1978). 8. Suuberg, E. M., Peters, W. A., and Howard, J. B., Seventeenth
Symposium
(International)
on Corn-
bustion, The Combustion Institute, Pittsburgh, 1979,
p. 117. 9. Solomon, P. R., and Colket, M. B,, Seventeenth Symposium (International} on Combustion, The Combustion Institute, Pittsburgh, 1979, p. 131.
Received 7 October 1982; revised 26 August 1983