I.W. Lenggoro et al.: An experimental and modeling investigation of particle production by spray pyrolysis
process. Marshall and colleagues6–12 investigated the ef-
phology. Moreover, neither their modeling results nor the
results of Jayanthi et al. are directly compared with ex-
perimental results.
fect of solvent evaporation rate on the morphology of
dried particles by deriving the diffusion equation for the
mass transfer of a dissovled solid inside a droplet. The
diffusion equations presented in Marshall’s paper6,7 were
too complicated to be solved analytically due to the mov-
ing boundary caused by the shrinkage of the droplet.
Thus, this initial work on mass transfer inside a droplet
employed several assumptions, which limited the use of
the solutions. The difficulty involved in the calculation of
the moving boundary problem was greatly simplified by
van der Lijn13 by proposing a mathematical relation for
fixing the outer boundary. This technique enables a
simple analytical relation for calculating the solute con-
centration distribution inside a droplet.
Most of these earlier studies were qualitative in nature
and usually examined relatively large particles of size
100 to 1000 m. Among the few studies for droplets of
size 10 to 100 m, Leong9 proposed that limited control
of particle morphology could be achieved by controlling
the temperature and humidity of the carrier gas as well as
the precursor solution characteristics.
Clearly, the formation of particles by spray pyrolysis is
a complex process and is difficult to accurately model.
The task is made more difficult by the lack of data on the
chemistry and solubility of many precursors, as well as
nucleation and crystallization during precipitation. It is
essential to develop a model that considers both multiple
droplets and changes in mass concentration within the
droplets. Until now, this important problem has been left
unsolved.
In this study, we present a model of the particle
formation process that is based on the models pres-
ented by Jayanthi et al.11 and Xiong and Kodas.12 Our
model simultaneously computes the evaporation rate
from a monodisperse population of aerosol particles
and the change of the solute concentration within the
droplets. The change in droplet size and particle mor-
phology is calculated as a function of position in the
reactor and process time. For experimental comparison,
zirconia particles were prepared using the spray-
pyrolysis process at a number of operating conditions.
Zirconia was selected because the wide application in
industry due to its outstanding mechanical strength, ther-
mal stability, chemical resistance, and electrical charac-
teristics. In addition, values of the material-property data
required for the modeling study are available in the
literature.11
Jayanthi et al.11 applied van der Lijn’s technique12 to
solve the diffusion equation inside the droplet to model
the evaporation and solute precipitation of 10-m zirco-
nia particles. They assumed that homogeneous nuclea-
tion would occur when the solute concentration at the
surface of the droplet reached the critical supersaturation.
After nucleation of the solid, precipitation occurs only in
the part of the droplet where the solute concentration is
higher than the equilibrium saturation. Hollow particles
result if the solute concentration at the center of the drop-
let is less than the equilibrium saturation of the solute.
Using their model, they predicted the morphology result-
ing from the spray pyrolysis of ZrO2 from zirconyl hy-
droxide chloride, a precursor for which they had
previously measured the values of the critical and equi-
librium saturations.14 Their calculations considered the
effects of parameters such as process temperature and the
initial solute concentration on the morphology of single
particles. They found that lower process temperatures
and higher initial solute concentrations favored the for-
mation of dense particles.
Of all the numerical studies of the droplet to particle
conversion process, only one considered the effect of
multiple droplets.12 Their calculations were performed
using sodium chloride as a model compound. They pre-
sented calculation results for the change of solvent vapor
concentration, droplet size, and droplet temperature dur-
ing heating in a laminar flow reactor by varying values
like the initial number concentration of ambient humid-
ity. However, their model did not consider the change of
mass concentration inside the droplets due to evapora-
tion. All droplets were assumed to form solid, dense
particles; no attempt was made to model particle mor-
II. EXPERIMENTAL PROCEDURE
A schematic of the experimental apparatus used to
produce and collect the zirconia particles is shown in
Fig. 1. The main equipment consists of (i) a nebulizer
that converts the starting solution into microdroplets, (ii)
the carrier gas, (iii) a tubular, laminar flow aerosol reac-
tor, and (iv) a sampler or precipitator. The starting solu-
tion was atomized at a frequency of 1.75 MHz by an
ultrasonic nebulizer (Omron Co., Kyoto, Japan, Model
NE-U11B), which was cooled with running water. The
level of the spray solution was kept constant to ensure a
uniform generation rate of droplets. Figure 2 shows the
equivalent volume diameter distribution of the atomized
water droplets as measured by a light-scattering particle-
size analyzer (Malvern Instruments Corp., Worcester-
shire, U.K., Mastersizer DPF). The average equivalent
volume diameter of solution droplets was 4.5 m. Wa-
ter was used as the solvent. The tubular furnace was
an alumina tube of 13-mm inside diameter and about
1000 mm long. The furnace consists of five indepen-
dently controlled heating zones, each 200 mm in length,
enabling flexibility in the production of the experimental
temperature distributions. The temperature of each heat-
ing zone was controlled to within 2 °C. A pre-
734
J. Mater. Res., Vol. 15, No. 3, Mar 2000
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