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1© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
Correspondence to: Reydick D. Balucan, Priority Research Centre for Energy, The University of Newcastle, Callaghan,
NSW 2308, Australia. E-mail: reydick.balucan@uon.edu.au
†This paper is part of the In Focus: Papers from ACEME10 - the Accelerated Carbonation for Environmental and
Materials Engineering conference issue.
Received June 6, 2011; revised and accepted July 21, 2011
Published online at Wiley Online Library (wileyonlinelibrary.com). DOI: 10.1002/ghg.33
Modeling and Analysis
Optimization of antigorite heat
pre-treatment via kinetic modeling
of the dehydroxylation reaction for
CO2 mineralization†
Reydick D. Balucan and Eric M. Kennedy, The University of Newcastle, Callaghan, NSW, Australia
John F. Mackie, The University of Newcastle and The University of Sydney, NSW, Australia
Bogdan Z. Dlugogorski, The University of Newcastle, Callaghan, NSW, Australia
Abstract: This contribution describes a predictive framework expedient to the thermal processing of
serpentinites for the mineralization of CO2. We demonstrate the optimization of heat treatment of
antigorite, providing a benchmark of an extreme case of activation among serpentine minerals. Antigo-
rite was investigated non-isothermally via thermogravimetry-mass spectrometry and in situ X-ray
powder diffraction, its thermal reaction sequence elucidated, and reaction kinetics subsequently
modeled. Based on the thermally induced structural changes, preferred content of residual hydroxyls
in the dehydroxylated antigorite amounts to 10–40% of those present initially. This degree of dehy-
droxylation minimized the transformation of antigorite into new crystalline phases maximizing the
amorphization of the new structure. The thermal reaction sequence provided both the explanation for
the observed kinetic behavior and the basis for this optimization strategy. The optimal time for heat
activation corresponds to ≤ 30 min, including the heat-up period at a rate of 30 °C min–1
and an iso-
thermal stage at 730 °C. This was successfully modeled using a three-dimensional phase boundary
reaction model (R3), with activation energy Ea of 160 kJ mol–1
and a frequency factor A of 5.7 ± 4.1 ×
105
s–1
(5.7 × 105
s–1
for dynamic and 1.6 × 105
s–1
for static stage). This strategy translates to a fast
and efficient thermal processing in an optimally sized calcining vessel. Furthermore, these results imply
that activation of the more common serpentine minerals lizardite and chrysotile would be significantly
faster as their dehydroxylation proceeds at lower temperatures than that of antigorite.
© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd
Keywords: activation; dehydroxylation; heat treatment; serpentinite
Introduction
T
he direct aqueous-phase mineralization of CO2
with heat-activated serpentine minerals is a
technologically feasible CO2 fixation solution and
arguably the best mineral carbonation process to-
date.1–9
On the other hand, its economic viability
remains vague.10
This uncertainty is largely due to
the energy requirements, in particular, the thermal
pre-treatment stage that is sometimes deemed
RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2
2 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
prohibitive and economically non-viable.11,12
It must
be noted, however, that previous energy and cost
estimates were based on electrical heating at 630 °C
for 2 h and generally implemented irrespective of the
serpentine mineral composition. Previous energy
calculations represented overestimates, that did not
distinguish between heat and power duties,13
and
considered no heat integration and/or recovery of
sensible and latent heat into the process. By using heat
instead of electricity in thermal pre-treatment, the
energy requirement can be lowered by at least ~ 30%.9
Furthermore, thermal treatment via direct heating
using heat of combustion with carbonaceous or
hydrocarbonaceous fuel is not only inexpensive and
more efficient as compared to electric heating,9,14
but
also allows for processing at higher temperatures.
Although thermal reactions of serpentine minerals
had been subjected to numerous studies,15–26
an
optimized processing strategy for CO2 mineralization
applications is scarce.27,28 In general, the enhanced
reactivity of thermally activated serpentine minerals
was attributed to the destruction of mineral crystal-
linity with the removal of structurally bound hy-
droxyl groups, resulting in improved Mg mobility in
the subsequent aqueous carbonation stage.27 This
information alone is insufficient and requires crucial
knowledge of the optimal structure for each ore and
its respective optimal dehydroxylation temperature.
These two dictate the required time (at a given heating
rate) necessary to design a practical dehydroxylation
process. The importance of mineral considerations, as
was exemplified by the huge disparity of serpentine
conversion on identically heat-treated serpentine
minerals, with antigorite achieving 92% while lizard-
ite only achieved 40%.11
Despite their mineralogical
differences both had been treated identically. It can
then be deduced that an optimal structure exists, and
varies from ore to ore. Once the idealized activated
structure for a particular feedstock has been identi-
fied, modeled, and predicted, only then can actual
energy requirements be reasonably estimated.
Serpentine dehydroxylation is complex and in-
cludes phase transition and formation of intermedi-
ate mineral phases.22,27
Obtaining the exact kinetic
data solely from non-isothermal thermogravimetry
is difficult, hence, in practice, one employs apparent
kinetic parameters. This approach relies on the
measurement of the overall weight change during the
dehydroxylation, as the evolution of water from
structurally bound hydroxyls relates to the degree of
dehydroxylation with time. Non-linear regression of
the derivative thermogravimetric curve then pro-
vides a direct and rapid method to estimate the
apparent kinetic parameters. The direct non-linear
regression reconstructs experimental measurements
more accurately than classical linearization meth-
ods.29,30
This is because the direct methods avoid the
assumption of high energy of activation and do not
rely on an incomplete expression of the Taylor
expansion.
Previous studies on serpentine kinetics do not reflect
the particle size of interest for direct aqueous mineral
carbonation, but rather involve either coarse
(> 150 μm) or too fine particles < 10 μm.17,19,20,25
Serpentine feedstock for direct aqueous carbonation
uses 38 to 75 μm particles to provide reasonable
reactivity at manageable energy penalties.2,4 The
reported activation energy values for serpentine
minerals vary from 184 to 630 kJ mol–1 in various
reaction mechanisms.17,19,20 This huge, and chemically
unrealistic, variation in activation energy had been
attributed to the presence of water vapor, differences
in experimental apparatus, processing history,
methods of kinetic analysis, ore purity and mineral
assemblages.15–21,23–25,31 In particular, the presence of
water vapor may engender a reverse reaction. If this
occurs, the rate measurements become a function of a
local concentration of water vapor, resulting in poorly
controlled experimental conditions, leading to
unreasonable values of activation energies derived
from such experiments. Fundamentally, the problem
resides in modeling the dehydroxylation process by a
forward step, whereas both forward and reverse steps
occur; i.e. the reaction takes place under near-
equilibrium conditions. Experiments must either be
performed under an imposed well-defined
concentration of water vapor or replicate runs must be
carried out at different flows of purge gas (as done in
the current study) to establish the validity of the
non-equilibrium conditions.
The present situation, of uncertain kinetic
parameters for dehydroxylation of serpentine
minerals, needs redressing, both for fundamental and
practical reasons. The latter would then facilitate the
prediction of the optimum processing conditions
appropriate for serpentine minerals to enable the
design of efficient unit operations for mineral
processing. In this study, we present a new set of
precise experimental measurements acquired under
well-controlled conditions, allowing us to develop
Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al.
3© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
accurate and practical models of serpentine
dehydroxylation. We used serpentinite which
contained mostly antigorite (antigorite has the highest
dehydroxylation temperature among serpentine
minerals) to represent the extreme case of thermal
activation.
The present contribution aims to demonstrate a
novel approach of optimizing the heat treatment stage
of serpentine minerals as feedstock for the direct
aqueous reaction with carbon dioxide. This involves
the identification of mineralogical changes associated
with the degree of dehydroxylation, elucidation of the
thermal reaction sequence and subsequently modeling
the kinetics of the reaction at the phenomenological
level. We then identify, predict, and validate the
optimal pre-treatment strategy for this particular
serpentinite sample, which consists of the desired
degree of dehydroxylation, optimal treatment tem-
perature, and reaction time.
Experimental
Antigorite-containing serpentinite, from the Great
Serpentine Belt of New South Wales, Australia, was
wet ground to 80% passing -75 μm, wet demagnetized,
dried at 105 °C, and then used in experiments without
further purification. Volumetric particle size distribu-
tion was determined by LALLS with Malvern Master-
sizer 2000 laser sizer, with measurements and valida-
tions conducted in aqueous media. Phase
identification by X-ray powder diffraction (XRPD)
was performed in Philips X’Pert Pro multipurpose
diffractometer using Cu Kα radiation in the range of
6-90° 2θ, with a step size of 0.02° and collection time
of 1 s step–1
. In situ hot-stage XRPD, at various
temperatures from 30–1100 °C each at 5 min scans,
was accomplished using an Anton Parr HTK16 fitted
with a platinum strip hot-stage. Temperature verifica-
tion was achieved by running standard minerals with
well-known phase reactions. The generated patterns
were matched against the International Centre for
Diffraction Data
®using X’pert Highscore
®, then
manually compared and checked for validity prior to
acceptance.32
A Spectro X’lab 2000 apparatus served
to analyze the chemical composition by polarized
energy dispersive X-ray fluorescence. Morphological
examination with scanning electron microscopy on
gold-coated samples was performed with Philips
XL30 SEM, operated at 15 kV and using a secondary
electron detector. Amdel Mineral Processing
Laboratories provided measurements for total organic
carbon and total carbon content.
Thermogravimetry analysis-mass spectrometry
(TGA-MS) for kinetic analysis was performed in a
Setaram Setsys Evolution 1200 TGA coupled to a
Pfeiffer Thermostar quadruple mass spectrometer.
Typically, samples of 5.50 ± 0.1 mg were heated in an
open alumina crucible under argon flowing at 20 and
200 ml min–1
, with imposed heating rates of 10, 20,
and 30 °C min–1
from 30 to 1000 °C. Duplicates for
kinetic runs were employed to ensure reproducibility
and accepted when within ± 0.1% of the total mass
loss. Blank runs involving empty crucibles for buoy-
ancy correction were carried out under identical
flow-rate and heating-rate to the actual kinetic runs.
The derivative thermogravimetric (DTG) curves were
then obtained via proprietary electronic differentia-
tion of the TG signal using the SetSoft 2000 software.
Kinetic analysis and modeling
Typical solid-state thermal processes, generally
represented by Eqn (1), involve heterogeneous decom-
position reactions. For kinetic studies, either an
appropriate flow of inert gas or vacuum is continu-
ously applied to the reaction system for immediate
depletion of any generated volatile products. This
negates reaction reversibility and ensures the reaction
occurring far from equilibrium. The mass change
with time then directly relates to the forward reaction
rate.
A(s) → B(s) + C(g) (1)
The reaction rate is commonly expressed in Eqn (2).
The temperature dependence of rate constant, k, is
given by the Arrhenius equation; where A is the
frequency factor, Ea the activation energy, T the
absolute temperature, R the gas constant, f(α) a
reaction or diffusion model (defined in Table 4 for the
present study), and α the conversion fraction.
kf( ) = Aexp
−E
RT
a
=
d
dt
α
α f( )α (2)
Equation (3) defines the fraction reacted, α, where mi,
mt and mf are initial mass, mass at time t and final
mass, respectively.
mi mt−
mi mf−
α = (3)
RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2
4 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
Simulation of the mass loss curve, for a particular
reaction model was carried out using Eqn (4). For
serpentinite, the DTG curves relate to the dehydroxy-
lation rate, where mc corresponds to the total mass of
evolved water.
m=
d
dt
m
sim
c
d
dt
α
= cm Aexp
−E
RT
a
f( )α− (4)
The apparent kinetic parameters were obtained via
non-linear regression employing the LM algorithm for
simultaneously fitting Ea and A using literature values
as initial estimations. This iterative solution method
minimized the sum of the squared difference between
the experimental DTG curve, −(dm/dt)exp, and the
fitted curve, −(dm/dt)sim (Eqn (5)). The quality of the
fitted parameters was assessed and accepted based on
the regression coefficient (r2), confidence intervals at
95% and residual plots.
OF
d
dt
m
exp
d
dt
m
sim
−= ∑
2
(5)
Model validations, predictions and simulations of
DTG curves were accomplished via RKF56 algorithm
to provide highly precise numerical solution for a
system of ordinary differential and algebraic
equations. Solvers for non-linear regression and
ordinary differential equations, embedded in POLY-
MATH 6.1 software, facilitated data processing.
Results and discussion
The serpentinite sample was predominantly crystal-
line antigorite (Antigorite-8.0M, ref. code: 00-007-
0417) with relatively minor phase of magnetite
(Triiron oxide, ref. code: 01-089-0691 and periclase
(MgO, ref. code: 01-077-2364). Following wet mag-
netic separation to remove magnetite, the serpentinite
ore grade was estimated at 98%. Figure 1 shows the
X-ray diffraction pattern of the sample before and
after demagnetization. As antigorite was the crystal-
line serpentine mineral identified, from now on the
serpentinite sample will be interchangeably referred to
as antigorite.
Characteristic volumetric size distribution, shown in
Table 1, reflects that of the targeted mineral carbon-
ation feed material at 80% passing 75 μm. This distri-
bution represented the comminution operation where a
mixture of fines and oversized particles was generated.
As shown in Table 2, chemical composition of the
demagnetized material is typical for antigorite, having
relatively low value of the loss on ignition at 1000 °C
and high Fe content among serpentine minerals. The
LOI1000v denotes mass of volatiles evolved from
Figure 1. X-ray powder diffraction patterns of natural and demagnetised serpentinite (antigorite). Intensity
of the demagnetised sample is stacked vertically by 20,000 units.
Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al.
5© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
mineral samples when heated to 1000 °C; usually, this
corresponds to free and crystalline water, as well as
CO2 from the decomposition of carbonates. Elemental
impurities include Al and trace amounts of Mn, Ca,
K, P, S, and Ti. Organic carbon comprises 0.3 mg g–1
while the inorganic carbon content is at 0.5 mg g–1
.
Should carbonate decomposition occur at the dehy-
droxylation region, the inorganic carbon content is no
more than 0.05%w/w, and is therefore negligible. Based
on this composition, a RCO2
value of 2.2, pertaining to
the minimum tonnage of mineral for fixing 1 tonne of
CO2 was calculated assuming complete (stoichiomet-
ric) carbonation of Mg and Fe.
Antigorite particles, as illustrated in Fig. 2, exhibited
angular morphology where edges and exposed
surfaces smoothened-out upon thermal treatment.
The well-known serpentine transformation to forster-
ite and enstatite is physically evident as a geometric
modification of the mineral. The formation of new
mineral phases normally proceeds via nucleation,
hence, in the kinetic analysis, this study employed
models of phase-boundary and nucleation reaction.
Figures 3(a)–3(b) confirm that the mass loss (11.4 ±
0.2%) results from the evolution of crystalline (hy-
droxyl-derived) water. No change in mass was ob-
served below 105 °C, indicating negligible content of
free water. Mass loss was prominent within the
500–800 °C region, bracketing the expected tempera-
ture range of antigorite dehydroxylation. The dehy-
droxylation rate attains maximum, -(dm/dt)max, of
(9.7 ± 0.3) × 10–4
mg s–1
, at around 730 °C. The
relatively high doublet peak temperature, Tp,33
charac-
teristic of antigorite, corresponds to Tp1 and Tp2 at
712 °C and 731 °C, respectively. These peaks signify
the subsequent formation of the mineral forsterite
(Mg2SiO4) and an intermediate phase (denoted as D2)
to be discussed in more detail in subsequent sections.
The in situ generated intermediate mineral phases
during the thermal treatment of antigorite, seen in
Fig. 4(a), were similarly observed for lizardite and
chrysotile.22,27 For antigorite, the formation of the
intermediate phases occur at relatively high tempera-
tures. The crystalline phase was predominantly
antigorite until 600 °C, where a low angle feature
appears at 6–7.5° 2θ. This reflection, corresponding to
d3,2 (µm) d4,3 (µm) d90 (µm) d50 (µm) d10 (µm)
5.31 44.2 128 16.0 1.86
Table 1. Volumetric particle size distribution
of the antigorite sample.
SiO2 MgO Fe2O3 Al2O3 CaO Na2O MnO SO3 P2O5 TiO2 K2O LOI1000
43.2 38.2 4.82 1.04 0.13 0.11 0.08 0.03 0.02 0.01 0.01 11.9
Table 2. Chemical composition of the antigorite sample by weight as % oxide.
Figure 2. SEM micrographs of (a) untreated and (b) thermally treated serpentinite
(antigorite).
RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2
6 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
d spacing of 14 Å, is likely caused by doubling of the
interlamellar spacing at (001) (d spacing = 7 Å).
Forsterite was then first observed by 725 °C. At
750 °C, another low angle feature appears at 7.5–
10° 2θ. This reflection corresponds to d spacing of
10 Å, and could be doubling of 17° 2θ reflection (d
spacing = 5 Å). The doubling of d spacings indicates
voids in the octahedral layers due to progressive
dehydroxylation. Both low-angle reflections were
designated similarly to the intermediates formed in
thermal treatment of chrysotile,22
as dehydroxylates 1
and 2 (D1 and D2). By 800 °C, characteristic reflec-
tions of antigorite along (001) and (002), correspond-
ing to 12 and 24° 2θ, disappear, signifying the collapse
of interlamellar spacings.
At higher temperatures ~ 800–825 °C, another
crystalline phase, corresponding to mineral enstatite
(MgSiO3) forms, and persists alongside forsterite. As a
chain silicate (pyroxene), estatite is unreactive to
carbonation.27,34
Hence, the reactivity of antigorite,
thermally treated in excess of 800 °C, will decline
proportionally to its enstatite content.
Numerical integration of the three main antigorite
reflections at 11–13, 24–26, 35–46° 2θ and one for
platinum at 65–67° 2θ produced a series of area
counts tracking antigorite dehydroxylation. The
antigorite-platinum ratio, as shown in Fig. 4(b),
follows that of the TGA-derived content of OH
content. This directly relates the OH content of the
bulk rock to the in situ generated phases via the
temperature measurements where these phases were
observed. Table 3 summarizes the corresponding
content of OH for the observed minerals phases.
Table 4 summarizes the apparent kinetic parameters,
where random nucleation model (F1) yields the highest
Ea and A values followed by the phase-boundary
Figure 4. Plots for (a) in-situ XRPD patterns at various temperatures and (b) correlation of non-isothermal XPRD
and TGA. The crystalline minerals and hypothetical intermediate phases are labelled as A: antigorite, D1:
dehydroxylate 1, D2 : dehydroxylate 2, F: forsterite and E: enstatite.
Figure 3. Typical curves for (a) TGA-DTG and (b) MS depicted as ion current intensities for H2O (m/z = 18) and CO2
(m/z = 44) during serpentinite (antigorite) dehydroxylation reaction.
Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al.
7© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
reaction mechanisms (R3) and (R2), respectively. The
Ea value for F1 model (193 ± 2 kJ mol–1) is slightly
lower than previously reported in literature for
serpentine at 202–502 kJ mol–1.17 Activation energy
for R2 model (134 ± 11 kJ mol–1 ) is closer to those
reported for brucite at 146 kJ mol–1,35 while the values
calculated from the R3 model (160 ± 7 kJ mol–1) fall
midway between those reported for brucite and
serpentine. The R3 model, besides providing better fit
in all three heating rates, was confirmed by morpho-
logical observations. Alternatively, the transformation
could initially follow R2 mechanism, shifting to
nucleation mechanism at later stages.
While the kinetic compensation effect (KCE),
including its validity and significance, is beyond the
scope of this paper, this mutual dependence of A and
Ea, were only observed for both R2 and R3 mecha-
nisms (a plot of ln A vs Ea yields a correlation coeffi-
cient r2
close to unity). The isokinetic temperatures, Ti,
for R2 and R3 were estimated at 489 °C and 474 °C,
respectively. While Ea and A values for phase bound-
ary reaction models systematically increased with
heating rate, the increase in Ea values were minimal
(within ~95% confidence interval) as compared to the
A values. This observed compensation effect is prob-
ably a mere computational artifact innate to the
deficiencies of extending the Arrhenius equation to
Table 3. In situ generated mineral phases and the
corresponding bulk % OH content of the rock.
Mineral Phase (in situ XRPD) OH content, % (TGA)
Antigorite 10–100
Dehydroxylate 1 10–88
Forsterite 0–30
Dehydroxylate 2 0–10
Enstatite 0
Heating rate,
°C min–1
Flow rate,
ml min–1
Parameters
Contracting
cylinder (R2)
f(α) = 2(1 − α)0.5
Contracting
sphere (R3)
f(α) = 3(1 − α)0.67
Random
nucleation (F1)
f(α) = (1 − α)
10
20
E, kJ mol–1
95% Confidence
122
5
151
7
196
0.08
A, s–1
95% Confidence
3.4 × 103
1.9 × 103
9.8 × 104
8.0 × 104
1.0 × 108
9.8 × 105
r2 0.8471 0.8969 0.8635
200
E, kJ mol–1
95% Confidence
119
5
146
7
196
0.08
A, s–1
95% Confidence
2.2 × 103
1.1 × 103
5.4 × 104
3.5 × 104
1.0 × 108
8.0 × 105
r2 0.8746 0.9245 0.8987
20 20
E, kJ mol–1
95% Confidence
139
6
164
6
193
0.01
A, s–1
95% Confidence
4.6 × 104
3.3 × 104
7.2 × 105
5.7 × 105
1.0 × 108
1.4 × 105
r2
0.9647 0.9633 0.8877
30 20
E, kJ mol–1
95% Confidence
142
7
164
8
191
0.13
A, s–1
95% Confidence
8.4 × 104
7.5 × 104
8.8 × 105
8.0 × 105
1.0 × 108
1.5 × 106
r2 0.9722 0.9680 0.9199
*Mean
E, kJ mol–1
σ
134
11
160
7
193
2
A, s–1
σ
4.4 × 104
4.1 × 104
5.7 × 105
4.1 × 105
1.0 × 108
0
*Mean values at heating rates of 10, 20, and 30 at a gas flow rate of 20 ml min–1
Table 4. Apparent kinetic parameters for R2, R3, and F1 models at various conditions.
RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2
8 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
solid-state kinetics. However, if it is not just a math-
ematical consequence, the larger range of A values
compared to Ea may indicate enhancements at high
heating rates largely driven by entropic and much less
by enthalpic contributions (KCE was previously
known as enthalpy-entropy compensation effect). This
means that while the threshold energy transferred
though lattice vibrations do not deviate substantially
with increased heating rates, the resulting increase in
vibratory frequency induces a more efficient release of
volatile component. To account for this effect in
subsequent model validations and predictions with R
models, the mean Ea values were used while A values
were adjusted (but maintained within the range
obtained) to correspond to the imposed heating rate.
As in the case of an isothermal stage, the lowest
possible A value within the obtained range (i.e. 1.6 ×
105
s–1
for R3’s 5.7 ± 4.1 × 105
s–1
) was used.
The kinetic parameters were validated via recon-
structions of the of the DTG curves (obtained using
heating rate of 10 °C min–1
) at the 400–800 °C region.
As clearly indicated in Figs 5(a–c), the R3 model
provided a good overall match to the experimental
measurements. The R3 reconstruction matched well
the peak region from 620–800 °C, overall curve shape,
−(dm/dt)max and Tp. While during dehydroxylation,
minerals may undergo several successive steps, only
the R3 mechanism provided a practical, physically
evident and phenomenologically valid model for
simulating the overall thermal behavior of antigorite.
Furthermore, the predictive capability of the R3
model was tested by simulating the effect of sample
Figure 5. Model validation via reconstructions of the experimental DTG curve using (a) contracting cylinder R2,
(b) contracting sphere R3 and (c) random nucleation model F1. Simulation of DTG curves using the R3 model to
predict the effects of (d) sample mass SMx and (e) heating rates HRy.
Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al.
9© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
Figure 6. Degree of dehydroxylation achieved during heat activation at (a) 730 °C showing the good agreement
between experimental and the R3 model prediction (Ea value of 160 kJ mol–1
and A of 5.7 × 105
s–1
for the
dynamic heating rate and 1.6 × 105
s–1
for static heating stage, respectively) and (b) experimentally observed
activation profile at 630 °C and 730 °C. Lizardite activation at 630 °C is included for comparison.
mass and heating rates. Figures 5(d) and 5(e)
demonstrated that these effects were well accounted
for, showing the increasing trend in the dehydroxyla-
tion rates for both process variables, yielding the
correct locations of the −(dm/dt)max and Tp.
Considering that thermal energy is provided directly
from combustion, high-grade heat allows for high
temperature operations. Heat activation of antigorite
is then best performed at the mineral Tp, where the
rate is at its maximum. This heat treatment at 730 °C
was then predicted using R3 with Ea of 160 kJ mol–1
antigorite and A of 5.7 × 105
s–1
for heat-up period at
30 °C min–1
and 1.6 × 105
s–1
for the isothermal stage.
Figure 6(a) shows the good agreement for the pre-
dicted and observed antigorite dehydroxylation
carried out at 730 °C. The overall heat treatment
process for antigorite, which consists of heat-up and
isothermal stages, is complete within 34 min. The
heat-up period, from 30 to 730 °C at 30 °C min–1
requires 24 min, while the isothermal stage at 730 °C
to attain 90% dehydroxylation adds 6 min to the
operation. During the heat-up period, approximately
60% of total hydroxyls were removed from
500–730 °C. Full dehydroxylation requires 10 min of
the isothermal operation at 730 °C. But such opera-
tion is undesirable, as mineral’s reactivity deteriorates
for dehydroxylation in excess of 90%.34
The duration and temperature of dehydroxylation
define the reactivity of the activated mineral during
dissolution step in the aqueous carbonation. It was
observed that ≤ 90% dehydroxylation leads to
optimal reactivity.34 Generally, 120 min had been
previously used to activate both antigorite and
lizardite, with particles −38 μm in size. However,
serpentine conversions were significantly higher for
antigorite at 92% than lizardite at 40%.11 To probe
this difference, we performed isothermal activation
at 630 °C for 2 h on the antigorite sample and on
another serpentinite containing lizardite as a major
phase (both from the Great Serpentinite Belt). Figure
6(b) shows that this heat pre-treatment fully dehy-
droxylated lizardite but only removed ~55% of
antigorite’s hydroxyl content. Furthermore, the
comparison of two activation temperatures for
antigorite point up to the differences in dehydroxyla-
tion rates at 730 °C and 630 °C. Although the opti-
mal degree of dehydroxylation to maximize conver-
sion requires experimental verification, the higher
conversion for antigorite compared to lizardite may
be attributed to the variation in the structural
composition of the two minerals.
At 40% OH content, only antigorite and dehydroxy-
late 1 were present (Table 3). Forsterite only starts to
form when OH content is less than 30%. At 90%
dehydroxylation, dehydroxylate 2 is visible while both
dehydroxylate 1 and antigorite disappear. This occurs
at 800 o
C, where, as seen from Fig. 4, the interlayer
spacings collapse. It can then be deduced that serpen-
tine activation must not exceed 90% dehydroxylation
to maintain an open, layered structure.
RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2
10 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
3. O’Connor WK, Dahlin DC, Rush GE, Gerdemann SJ and
Penner LR, Energy and Economic Considerations for Ex-situ
Aqueous Mineral Carbonation, DOE/ARC-2004-028 US
Department of Energy, Albany Research Center, Albany, OR,
USA (2004).
4. O’Connor WK, Dahlin DC, Rush GE, Gerdemann SJ, Penner
LR and Nilsen RP, Aqueous Mineral Carbonation: Mineral
Availability, Pre-treatment, Reaction Parametrics, and Process
Studies, DOE/ARC-TR-04-002. Albany Research Center,
Albany, OR, USA (2005).
5. O’Connor WK, Dahlin DC, Nilsen RP, Rush GE, Walters RP
and Turner PC, CO2 storage in solid form: A study of direct
mineral carbonation, DOE/ARC-2000-011, in Proceedings of
the 5th International Conference on Greenhouse Gas
Technologies, August 14–18, 2000, Cairns, Australia (2000).
6. O’Connor WK, Dahlin DC, Nilsen RP and Gerdemann SJ,
Continuing studies on direct aqueous mineral carbonation for
CO2 sequestration, in Proceedings of the 27th International
Technical Conference on Coal Utilization and Fuel Systems,
March 4–7, 2002, Clearwater, FL, USA (2002).
7. O’Connor WK, Dahlin DC, Nilsen RP and Turner PC, Carbon
dioxide sequestration by direct mineral carbonation with
carbonic acid, in Proceedings of the 25th International
Technical Conf. on Coal Utilization and Fuel Systems, March
6–9, 2000, Clearwater, FL, USA ( 2000).
8. O’Connor WK, Dahlin DC, Nilsen RP, Rush GE, Walters RP
and Turner PC, Carbon dioxide sequestration by direct
mineral carbonation: Results from recent studies and current
status, in Proceedings of the 1st National Conference on
Carbon Sequestration, DOE/ARC-2001-029, May 14–17, 2001,
National Energy Technology Laboratory, Department of
Energy, Washington DC, USA (2001).
9. Sipilä J, Teir S and Zevenhoven R, Carbon Dioxide Sequestra-
tion by Mineral Carbonation - Literature Review Update,
Report VT 2008-1.[Online]. Åbo Akademi University, Heat
Engineering Laboratory, Turku, Finland, 2008. Available at:
http://web.abo.fi/~rzeve nho/MineralCarbonationLiterature
Review05-07.pdf [October 21, 2009]
10. IPCC, Special Report on Carbon Capture and Storage,
ed by Metz B, Davidson O, de Coninck HC, Loos M, and
Meyer LA. Cambridge University Press, Cambridge, UK
(2005).
11. Gerdemann SJ, O’Connor WK, Dahlin DC, Penner LR and
Rush H, Ex situ aqueous mineral carbonation. Environ Sci
Technol 41:2587–2593 (2007).
12. Khoo HH and Tan RBH, Life cycle evaluation of CO2 recovery
and mineral sequestration alternatives. Environ Progress
25:208–217 (2006).
13. Zevenhoven R, Fagerlund J and Songkok JK, CO2 mineral
sequestration: Developments towards large-scale application.
Greenhouse Gas Sci Technol. 1:48–57 (2011).
14. Brent G, Integrated Chemical Process. Patent
WO/2008/0631305 A1 (2008).
15. Ball MC and Taylor HFW, The dehydration of chrysotile in air
and under hydrothermal conditions. Mineral Mag 33:467–482
(1963).
16. Brindley GW and Hayami R, Kinetics and mechanisms of
dehydration and recrystallization of serpentine: I, in Proceed-
ings of the 12th National Conference on Clays and Clay
Minerals, September 30 – October 2, 1963, Atlanta, GA (1964).
17. Brindley GW, Narahari Achar BN and Sharp JH, Kinetics and
mechanism of dehydroxylation processes: II. Temperature
Conclusion
In this study, we demonstrated the optimization of
antigorite heat treatment, providing a benchmark of
an extreme case of activation among serpentine
minerals. This was made via the development of a
novel predictive framework, affording the optimisa-
tion of the dehydroxylation process as function of
processing temperature and residence time to provide
a methodology for designing practical unit operations
for thermal processing of serpentinite ores. Based on
the observed structural changes, a properly activated
antigorite appears to contain between 10 and 40%
residual hydroxyls. The optimum activation strategy
inferred from the combined kinetic and mechanistic
considerations amounts to the production of a 60–
90% dehydroxylated mineral, isothermally at 730 °C
for ≤ 6 min. On the other hand, the present results
indicate that the reason of low activity of lizardite,
reported in literature,11 rests with excessive duration
of activation that led to the collapse in the mineral
structure and formation of relatively unreactive
enstatite upon full dehydroxylation. Generally, the
suggested heat treatment strategy translates to a fast
and efficient thermal processing in an optimally sized
calcining vessel. The activation of the more common
serpentine minerals lizardite and chrysotile is ex-
pected to be significantly faster as dehydroxylation
proceeds at lower temperatures than antigorite. Due
to mineralogical differences and composition of
serpentinites, heat treatment and its optimization
must be unique for each ore.
Acknowledgements
This study was funded in part by an internal grant
(Ref. No. G0189103) from the University of Newcastle.
D. Phelan and J. Zobec (EM-X-ray Unit, University of
Newcastle) assisted with SEM, XRF and XRD analy-
ses. Discussions with Prof. Erich Kisi, Dr Judy Bailey,
and Ms Monica Davis are greatly appreciated. Reydick
Balucan thanks the University of Newcastle for the
postgraduate research scholarship.
References
1. Huijen WJJ and Comans RNJ, Carbon Dioxide Sequestration by
Mineral Carbonation. Report No. ECN-C--03-016. ECN (Energy
Research Centre of Netherlands), the Netherlands (2003).
2. Huijen WJJ and Comans RNJ, Carbon Dioxide Sequestration
by Mineral Carbonation. Report No. ECN-C--05-022. ECN
(Energy Research Centre of Netherlands), the Netherlands
(2005).
Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al.
11© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg
and vapor pressure dependence of dehydroxylation of
serpentine. Am Mineral 52:1697–1705 (1967).
18. Candela PA, Crummett CD, Earnest DJ, Frank MR and Wylie
AG, Low pressure decomposition of chrysotile as a function
of time and temperature. Am Mineral 92:1704–1713 (2007).
19. Cataneo A, Gualteri AF and Artioli G, Kinetic study of the
dehydration of chrysotile asbestos with temperature by in situ
XRPD. Phys Chem Miner 30:177–183 (2003).
20. Llanna-Fúnez LS, Brodie KH, Rutter EH and Arkwright JC,
Experimental dehydration kinetics of serpentine using pore
volumometry. J Metamorphic Geol 25:423–438 (2007).
21. Inque T, Yoshimi I, Yamada A and Kikegawa T, Time-resolved
X-ray diffraction analysis of the experimental dehydration of
serpentine at high pressure. Mineral Petrol Sci 104:105–109
(2009).
22. MacKenzie KJD and Meinhold RH, Thermal reactions of
chrysotile revisted: A 29Si and 25Mg MAS NMR study. Am
Mineral 79:43–50 (1994).
23. Perrillat JP, Daniel I, Koga KT, Reynard B, Cardon H and
Crichton WA, Kinetics of antigorite dehydration: A real-time
X-ray diffraction study. Earth Planet Sci Lett 236:899–913
(2005).
24. Tyburczy JA and Ahrens T, Dehydration kinetics of shocked
serpentine, in Proceedings of the 18th
Lunar and Planetary
Science Conference, March 16–20, 1987, Houston, TX (1988).
25. Weber JN and Greer RT, Dehydration of serpentine: Heat of
reaction and reaction kinetics at PH2O = 1 atm. Am Mineral
50:450–464 (1965).
26. Chizmeshya AVG, McKelvy MJ, Sharma R, Carpenter RW and
Bearat H, Density functional theory study of the decomposi-
tion of Mg(OH)2: A lamellar dehydroxylation model. Mater
Chem Phys 77:416–425 (2002).
27. McKelvy MJ, Chizmeshya AVG, Diefenbacher J, Bearat H and
Wolf G, Exploration of the role of heat activation in enhancing
serpentine carbon sequestration reactions. Environ Sci
Technol 38:6897–6903 (2004).
28. McKelvy MJ, Sharma R and Chizmeshya AVG, Lamellar
reaction phenomena: From intercalation to nanomaterials
formation. J Phys Chem Solids 67:888–895 (2006).
29. Ferriol M, Gentilhomme A, Cochez M, Oget N and
Mieloszynski JL, Thermal degradation of poly(methyl
methacrylate) (PMMA): Modelling of DTG and TG curves.
Polym Degrad Stabil 79:271–281 (2003).
30. Yang J, Miranda R and Roy C, Using the DTG curve fitting
method to determine the apparent kinetic parameters of
thermal decomposition of polymers. Polym Degrad Stabil
73:455–461 (2000).
31. Martinez E, The effect of particle size on the thermal properties
of serpentine minerals. Am Mineral 46:901–912 (1961).
32. Wicks FJ, Status of the reference X-ray powder-diffraction
patterns for the serpentine minerals in the PDF data-
base-1997. Powder Diffr 15:42–50 (2000).
33. Viti C, Serpentine minerals discrimination by thermal analysis.
Am Mineral 95:631–638 (2010).
34. Li W, Li W, Li B and Bai Z, Electrolysis and heat pre-treatment
methods to promote CO2 sequestration by mineral carbon-
ation. Chem Eng Res Des 87:210–215 (2009).
35. Butt DP, Lackner KS, Wendt CH, Conzone SD, Kung H, Lu Y
and Bremser JK, Kinetics of thermal dehydroxylation and
carbonation of magnesium hydroxide. J Am Ceram Soc
79:1892–1898 (1996).
Reydick Balucan
Reydick D. Balucan is a post-graduate
researcher working on mineral carbon-
ation at the Priority Research Centre
for Energy, University of Newcastle.
His focus is in the optimization of
direct aqueous mineral carbonation of
serpentine minerals. He holds a BSc in
Chemistry from Negros Oriental State University
(Philippines) and will finish his PhD (Chemical Engineer-
ing) by 2012.
Eric Kennedy
Professor Eric M. Kennedy is the
Deputy Director of the Priority Re-
search Centre for Energy, The Univer-
sity of Newcastle. He holds a BSc
(New South Wales) in Pure and
Applied Chemistry and a PhD (New
South Wales) in Physical Chemistry.
His interests include mitigation of ozone-depleting
gases as well as CO2 capture and storage.
John Mackie
Professor John F. Mackie is a conjoint
professor in Chemical Engineering at
the University of Newcastle. He holds
a DSc (Sydney) in Chemistry. He
specializes in chemical kinetics,
quantum chemistry and high tempera-
ture chemistry. He is a member of the
Priority Research Centre for Energy, University of
Newcastle.
Bogdan Dlugogorski
Prof. Bogdan Z. Dlugogorski is a
Fellow of the Australian Academy of
Technological Sciences and Engineer-
ing and the Director of the Priority
Research Centre for Energy, University
of Newcastle. He holds a BSc (Cal-
gary) in Chemical Engineering and
Geophysics, and an MEng (McGill), a PhD (Montreal)
and a DSc (Newcastle). His research interests are in
process safety and environment protection, including
CO2 storage.

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Balucan_2011_Optimization of antigorite heat pre-treatment via kinetics modeling of the dehydroxylation reaction for CO2 minera

  • 1. 1© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg Correspondence to: Reydick D. Balucan, Priority Research Centre for Energy, The University of Newcastle, Callaghan, NSW 2308, Australia. E-mail: reydick.balucan@uon.edu.au †This paper is part of the In Focus: Papers from ACEME10 - the Accelerated Carbonation for Environmental and Materials Engineering conference issue. Received June 6, 2011; revised and accepted July 21, 2011 Published online at Wiley Online Library (wileyonlinelibrary.com). DOI: 10.1002/ghg.33 Modeling and Analysis Optimization of antigorite heat pre-treatment via kinetic modeling of the dehydroxylation reaction for CO2 mineralization† Reydick D. Balucan and Eric M. Kennedy, The University of Newcastle, Callaghan, NSW, Australia John F. Mackie, The University of Newcastle and The University of Sydney, NSW, Australia Bogdan Z. Dlugogorski, The University of Newcastle, Callaghan, NSW, Australia Abstract: This contribution describes a predictive framework expedient to the thermal processing of serpentinites for the mineralization of CO2. We demonstrate the optimization of heat treatment of antigorite, providing a benchmark of an extreme case of activation among serpentine minerals. Antigo- rite was investigated non-isothermally via thermogravimetry-mass spectrometry and in situ X-ray powder diffraction, its thermal reaction sequence elucidated, and reaction kinetics subsequently modeled. Based on the thermally induced structural changes, preferred content of residual hydroxyls in the dehydroxylated antigorite amounts to 10–40% of those present initially. This degree of dehy- droxylation minimized the transformation of antigorite into new crystalline phases maximizing the amorphization of the new structure. The thermal reaction sequence provided both the explanation for the observed kinetic behavior and the basis for this optimization strategy. The optimal time for heat activation corresponds to ≤ 30 min, including the heat-up period at a rate of 30 °C min–1 and an iso- thermal stage at 730 °C. This was successfully modeled using a three-dimensional phase boundary reaction model (R3), with activation energy Ea of 160 kJ mol–1 and a frequency factor A of 5.7 ± 4.1 × 105 s–1 (5.7 × 105 s–1 for dynamic and 1.6 × 105 s–1 for static stage). This strategy translates to a fast and efficient thermal processing in an optimally sized calcining vessel. Furthermore, these results imply that activation of the more common serpentine minerals lizardite and chrysotile would be significantly faster as their dehydroxylation proceeds at lower temperatures than that of antigorite. © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd Keywords: activation; dehydroxylation; heat treatment; serpentinite Introduction T he direct aqueous-phase mineralization of CO2 with heat-activated serpentine minerals is a technologically feasible CO2 fixation solution and arguably the best mineral carbonation process to- date.1–9 On the other hand, its economic viability remains vague.10 This uncertainty is largely due to the energy requirements, in particular, the thermal pre-treatment stage that is sometimes deemed
  • 2. RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 2 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg prohibitive and economically non-viable.11,12 It must be noted, however, that previous energy and cost estimates were based on electrical heating at 630 °C for 2 h and generally implemented irrespective of the serpentine mineral composition. Previous energy calculations represented overestimates, that did not distinguish between heat and power duties,13 and considered no heat integration and/or recovery of sensible and latent heat into the process. By using heat instead of electricity in thermal pre-treatment, the energy requirement can be lowered by at least ~ 30%.9 Furthermore, thermal treatment via direct heating using heat of combustion with carbonaceous or hydrocarbonaceous fuel is not only inexpensive and more efficient as compared to electric heating,9,14 but also allows for processing at higher temperatures. Although thermal reactions of serpentine minerals had been subjected to numerous studies,15–26 an optimized processing strategy for CO2 mineralization applications is scarce.27,28 In general, the enhanced reactivity of thermally activated serpentine minerals was attributed to the destruction of mineral crystal- linity with the removal of structurally bound hy- droxyl groups, resulting in improved Mg mobility in the subsequent aqueous carbonation stage.27 This information alone is insufficient and requires crucial knowledge of the optimal structure for each ore and its respective optimal dehydroxylation temperature. These two dictate the required time (at a given heating rate) necessary to design a practical dehydroxylation process. The importance of mineral considerations, as was exemplified by the huge disparity of serpentine conversion on identically heat-treated serpentine minerals, with antigorite achieving 92% while lizard- ite only achieved 40%.11 Despite their mineralogical differences both had been treated identically. It can then be deduced that an optimal structure exists, and varies from ore to ore. Once the idealized activated structure for a particular feedstock has been identi- fied, modeled, and predicted, only then can actual energy requirements be reasonably estimated. Serpentine dehydroxylation is complex and in- cludes phase transition and formation of intermedi- ate mineral phases.22,27 Obtaining the exact kinetic data solely from non-isothermal thermogravimetry is difficult, hence, in practice, one employs apparent kinetic parameters. This approach relies on the measurement of the overall weight change during the dehydroxylation, as the evolution of water from structurally bound hydroxyls relates to the degree of dehydroxylation with time. Non-linear regression of the derivative thermogravimetric curve then pro- vides a direct and rapid method to estimate the apparent kinetic parameters. The direct non-linear regression reconstructs experimental measurements more accurately than classical linearization meth- ods.29,30 This is because the direct methods avoid the assumption of high energy of activation and do not rely on an incomplete expression of the Taylor expansion. Previous studies on serpentine kinetics do not reflect the particle size of interest for direct aqueous mineral carbonation, but rather involve either coarse (> 150 μm) or too fine particles < 10 μm.17,19,20,25 Serpentine feedstock for direct aqueous carbonation uses 38 to 75 μm particles to provide reasonable reactivity at manageable energy penalties.2,4 The reported activation energy values for serpentine minerals vary from 184 to 630 kJ mol–1 in various reaction mechanisms.17,19,20 This huge, and chemically unrealistic, variation in activation energy had been attributed to the presence of water vapor, differences in experimental apparatus, processing history, methods of kinetic analysis, ore purity and mineral assemblages.15–21,23–25,31 In particular, the presence of water vapor may engender a reverse reaction. If this occurs, the rate measurements become a function of a local concentration of water vapor, resulting in poorly controlled experimental conditions, leading to unreasonable values of activation energies derived from such experiments. Fundamentally, the problem resides in modeling the dehydroxylation process by a forward step, whereas both forward and reverse steps occur; i.e. the reaction takes place under near- equilibrium conditions. Experiments must either be performed under an imposed well-defined concentration of water vapor or replicate runs must be carried out at different flows of purge gas (as done in the current study) to establish the validity of the non-equilibrium conditions. The present situation, of uncertain kinetic parameters for dehydroxylation of serpentine minerals, needs redressing, both for fundamental and practical reasons. The latter would then facilitate the prediction of the optimum processing conditions appropriate for serpentine minerals to enable the design of efficient unit operations for mineral processing. In this study, we present a new set of precise experimental measurements acquired under well-controlled conditions, allowing us to develop
  • 3. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al. 3© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg accurate and practical models of serpentine dehydroxylation. We used serpentinite which contained mostly antigorite (antigorite has the highest dehydroxylation temperature among serpentine minerals) to represent the extreme case of thermal activation. The present contribution aims to demonstrate a novel approach of optimizing the heat treatment stage of serpentine minerals as feedstock for the direct aqueous reaction with carbon dioxide. This involves the identification of mineralogical changes associated with the degree of dehydroxylation, elucidation of the thermal reaction sequence and subsequently modeling the kinetics of the reaction at the phenomenological level. We then identify, predict, and validate the optimal pre-treatment strategy for this particular serpentinite sample, which consists of the desired degree of dehydroxylation, optimal treatment tem- perature, and reaction time. Experimental Antigorite-containing serpentinite, from the Great Serpentine Belt of New South Wales, Australia, was wet ground to 80% passing -75 μm, wet demagnetized, dried at 105 °C, and then used in experiments without further purification. Volumetric particle size distribu- tion was determined by LALLS with Malvern Master- sizer 2000 laser sizer, with measurements and valida- tions conducted in aqueous media. Phase identification by X-ray powder diffraction (XRPD) was performed in Philips X’Pert Pro multipurpose diffractometer using Cu Kα radiation in the range of 6-90° 2θ, with a step size of 0.02° and collection time of 1 s step–1 . In situ hot-stage XRPD, at various temperatures from 30–1100 °C each at 5 min scans, was accomplished using an Anton Parr HTK16 fitted with a platinum strip hot-stage. Temperature verifica- tion was achieved by running standard minerals with well-known phase reactions. The generated patterns were matched against the International Centre for Diffraction Data ®using X’pert Highscore ®, then manually compared and checked for validity prior to acceptance.32 A Spectro X’lab 2000 apparatus served to analyze the chemical composition by polarized energy dispersive X-ray fluorescence. Morphological examination with scanning electron microscopy on gold-coated samples was performed with Philips XL30 SEM, operated at 15 kV and using a secondary electron detector. Amdel Mineral Processing Laboratories provided measurements for total organic carbon and total carbon content. Thermogravimetry analysis-mass spectrometry (TGA-MS) for kinetic analysis was performed in a Setaram Setsys Evolution 1200 TGA coupled to a Pfeiffer Thermostar quadruple mass spectrometer. Typically, samples of 5.50 ± 0.1 mg were heated in an open alumina crucible under argon flowing at 20 and 200 ml min–1 , with imposed heating rates of 10, 20, and 30 °C min–1 from 30 to 1000 °C. Duplicates for kinetic runs were employed to ensure reproducibility and accepted when within ± 0.1% of the total mass loss. Blank runs involving empty crucibles for buoy- ancy correction were carried out under identical flow-rate and heating-rate to the actual kinetic runs. The derivative thermogravimetric (DTG) curves were then obtained via proprietary electronic differentia- tion of the TG signal using the SetSoft 2000 software. Kinetic analysis and modeling Typical solid-state thermal processes, generally represented by Eqn (1), involve heterogeneous decom- position reactions. For kinetic studies, either an appropriate flow of inert gas or vacuum is continu- ously applied to the reaction system for immediate depletion of any generated volatile products. This negates reaction reversibility and ensures the reaction occurring far from equilibrium. The mass change with time then directly relates to the forward reaction rate. A(s) → B(s) + C(g) (1) The reaction rate is commonly expressed in Eqn (2). The temperature dependence of rate constant, k, is given by the Arrhenius equation; where A is the frequency factor, Ea the activation energy, T the absolute temperature, R the gas constant, f(α) a reaction or diffusion model (defined in Table 4 for the present study), and α the conversion fraction. kf( ) = Aexp −E RT a = d dt α α f( )α (2) Equation (3) defines the fraction reacted, α, where mi, mt and mf are initial mass, mass at time t and final mass, respectively. mi mt− mi mf− α = (3)
  • 4. RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 4 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg Simulation of the mass loss curve, for a particular reaction model was carried out using Eqn (4). For serpentinite, the DTG curves relate to the dehydroxy- lation rate, where mc corresponds to the total mass of evolved water. m= d dt m sim c d dt α = cm Aexp −E RT a f( )α− (4) The apparent kinetic parameters were obtained via non-linear regression employing the LM algorithm for simultaneously fitting Ea and A using literature values as initial estimations. This iterative solution method minimized the sum of the squared difference between the experimental DTG curve, −(dm/dt)exp, and the fitted curve, −(dm/dt)sim (Eqn (5)). The quality of the fitted parameters was assessed and accepted based on the regression coefficient (r2), confidence intervals at 95% and residual plots. OF d dt m exp d dt m sim −= ∑ 2 (5) Model validations, predictions and simulations of DTG curves were accomplished via RKF56 algorithm to provide highly precise numerical solution for a system of ordinary differential and algebraic equations. Solvers for non-linear regression and ordinary differential equations, embedded in POLY- MATH 6.1 software, facilitated data processing. Results and discussion The serpentinite sample was predominantly crystal- line antigorite (Antigorite-8.0M, ref. code: 00-007- 0417) with relatively minor phase of magnetite (Triiron oxide, ref. code: 01-089-0691 and periclase (MgO, ref. code: 01-077-2364). Following wet mag- netic separation to remove magnetite, the serpentinite ore grade was estimated at 98%. Figure 1 shows the X-ray diffraction pattern of the sample before and after demagnetization. As antigorite was the crystal- line serpentine mineral identified, from now on the serpentinite sample will be interchangeably referred to as antigorite. Characteristic volumetric size distribution, shown in Table 1, reflects that of the targeted mineral carbon- ation feed material at 80% passing 75 μm. This distri- bution represented the comminution operation where a mixture of fines and oversized particles was generated. As shown in Table 2, chemical composition of the demagnetized material is typical for antigorite, having relatively low value of the loss on ignition at 1000 °C and high Fe content among serpentine minerals. The LOI1000v denotes mass of volatiles evolved from Figure 1. X-ray powder diffraction patterns of natural and demagnetised serpentinite (antigorite). Intensity of the demagnetised sample is stacked vertically by 20,000 units.
  • 5. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al. 5© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg mineral samples when heated to 1000 °C; usually, this corresponds to free and crystalline water, as well as CO2 from the decomposition of carbonates. Elemental impurities include Al and trace amounts of Mn, Ca, K, P, S, and Ti. Organic carbon comprises 0.3 mg g–1 while the inorganic carbon content is at 0.5 mg g–1 . Should carbonate decomposition occur at the dehy- droxylation region, the inorganic carbon content is no more than 0.05%w/w, and is therefore negligible. Based on this composition, a RCO2 value of 2.2, pertaining to the minimum tonnage of mineral for fixing 1 tonne of CO2 was calculated assuming complete (stoichiomet- ric) carbonation of Mg and Fe. Antigorite particles, as illustrated in Fig. 2, exhibited angular morphology where edges and exposed surfaces smoothened-out upon thermal treatment. The well-known serpentine transformation to forster- ite and enstatite is physically evident as a geometric modification of the mineral. The formation of new mineral phases normally proceeds via nucleation, hence, in the kinetic analysis, this study employed models of phase-boundary and nucleation reaction. Figures 3(a)–3(b) confirm that the mass loss (11.4 ± 0.2%) results from the evolution of crystalline (hy- droxyl-derived) water. No change in mass was ob- served below 105 °C, indicating negligible content of free water. Mass loss was prominent within the 500–800 °C region, bracketing the expected tempera- ture range of antigorite dehydroxylation. The dehy- droxylation rate attains maximum, -(dm/dt)max, of (9.7 ± 0.3) × 10–4 mg s–1 , at around 730 °C. The relatively high doublet peak temperature, Tp,33 charac- teristic of antigorite, corresponds to Tp1 and Tp2 at 712 °C and 731 °C, respectively. These peaks signify the subsequent formation of the mineral forsterite (Mg2SiO4) and an intermediate phase (denoted as D2) to be discussed in more detail in subsequent sections. The in situ generated intermediate mineral phases during the thermal treatment of antigorite, seen in Fig. 4(a), were similarly observed for lizardite and chrysotile.22,27 For antigorite, the formation of the intermediate phases occur at relatively high tempera- tures. The crystalline phase was predominantly antigorite until 600 °C, where a low angle feature appears at 6–7.5° 2θ. This reflection, corresponding to d3,2 (µm) d4,3 (µm) d90 (µm) d50 (µm) d10 (µm) 5.31 44.2 128 16.0 1.86 Table 1. Volumetric particle size distribution of the antigorite sample. SiO2 MgO Fe2O3 Al2O3 CaO Na2O MnO SO3 P2O5 TiO2 K2O LOI1000 43.2 38.2 4.82 1.04 0.13 0.11 0.08 0.03 0.02 0.01 0.01 11.9 Table 2. Chemical composition of the antigorite sample by weight as % oxide. Figure 2. SEM micrographs of (a) untreated and (b) thermally treated serpentinite (antigorite).
  • 6. RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 6 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg d spacing of 14 Å, is likely caused by doubling of the interlamellar spacing at (001) (d spacing = 7 Å). Forsterite was then first observed by 725 °C. At 750 °C, another low angle feature appears at 7.5– 10° 2θ. This reflection corresponds to d spacing of 10 Å, and could be doubling of 17° 2θ reflection (d spacing = 5 Å). The doubling of d spacings indicates voids in the octahedral layers due to progressive dehydroxylation. Both low-angle reflections were designated similarly to the intermediates formed in thermal treatment of chrysotile,22 as dehydroxylates 1 and 2 (D1 and D2). By 800 °C, characteristic reflec- tions of antigorite along (001) and (002), correspond- ing to 12 and 24° 2θ, disappear, signifying the collapse of interlamellar spacings. At higher temperatures ~ 800–825 °C, another crystalline phase, corresponding to mineral enstatite (MgSiO3) forms, and persists alongside forsterite. As a chain silicate (pyroxene), estatite is unreactive to carbonation.27,34 Hence, the reactivity of antigorite, thermally treated in excess of 800 °C, will decline proportionally to its enstatite content. Numerical integration of the three main antigorite reflections at 11–13, 24–26, 35–46° 2θ and one for platinum at 65–67° 2θ produced a series of area counts tracking antigorite dehydroxylation. The antigorite-platinum ratio, as shown in Fig. 4(b), follows that of the TGA-derived content of OH content. This directly relates the OH content of the bulk rock to the in situ generated phases via the temperature measurements where these phases were observed. Table 3 summarizes the corresponding content of OH for the observed minerals phases. Table 4 summarizes the apparent kinetic parameters, where random nucleation model (F1) yields the highest Ea and A values followed by the phase-boundary Figure 4. Plots for (a) in-situ XRPD patterns at various temperatures and (b) correlation of non-isothermal XPRD and TGA. The crystalline minerals and hypothetical intermediate phases are labelled as A: antigorite, D1: dehydroxylate 1, D2 : dehydroxylate 2, F: forsterite and E: enstatite. Figure 3. Typical curves for (a) TGA-DTG and (b) MS depicted as ion current intensities for H2O (m/z = 18) and CO2 (m/z = 44) during serpentinite (antigorite) dehydroxylation reaction.
  • 7. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al. 7© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg reaction mechanisms (R3) and (R2), respectively. The Ea value for F1 model (193 ± 2 kJ mol–1) is slightly lower than previously reported in literature for serpentine at 202–502 kJ mol–1.17 Activation energy for R2 model (134 ± 11 kJ mol–1 ) is closer to those reported for brucite at 146 kJ mol–1,35 while the values calculated from the R3 model (160 ± 7 kJ mol–1) fall midway between those reported for brucite and serpentine. The R3 model, besides providing better fit in all three heating rates, was confirmed by morpho- logical observations. Alternatively, the transformation could initially follow R2 mechanism, shifting to nucleation mechanism at later stages. While the kinetic compensation effect (KCE), including its validity and significance, is beyond the scope of this paper, this mutual dependence of A and Ea, were only observed for both R2 and R3 mecha- nisms (a plot of ln A vs Ea yields a correlation coeffi- cient r2 close to unity). The isokinetic temperatures, Ti, for R2 and R3 were estimated at 489 °C and 474 °C, respectively. While Ea and A values for phase bound- ary reaction models systematically increased with heating rate, the increase in Ea values were minimal (within ~95% confidence interval) as compared to the A values. This observed compensation effect is prob- ably a mere computational artifact innate to the deficiencies of extending the Arrhenius equation to Table 3. In situ generated mineral phases and the corresponding bulk % OH content of the rock. Mineral Phase (in situ XRPD) OH content, % (TGA) Antigorite 10–100 Dehydroxylate 1 10–88 Forsterite 0–30 Dehydroxylate 2 0–10 Enstatite 0 Heating rate, °C min–1 Flow rate, ml min–1 Parameters Contracting cylinder (R2) f(α) = 2(1 − α)0.5 Contracting sphere (R3) f(α) = 3(1 − α)0.67 Random nucleation (F1) f(α) = (1 − α) 10 20 E, kJ mol–1 95% Confidence 122 5 151 7 196 0.08 A, s–1 95% Confidence 3.4 × 103 1.9 × 103 9.8 × 104 8.0 × 104 1.0 × 108 9.8 × 105 r2 0.8471 0.8969 0.8635 200 E, kJ mol–1 95% Confidence 119 5 146 7 196 0.08 A, s–1 95% Confidence 2.2 × 103 1.1 × 103 5.4 × 104 3.5 × 104 1.0 × 108 8.0 × 105 r2 0.8746 0.9245 0.8987 20 20 E, kJ mol–1 95% Confidence 139 6 164 6 193 0.01 A, s–1 95% Confidence 4.6 × 104 3.3 × 104 7.2 × 105 5.7 × 105 1.0 × 108 1.4 × 105 r2 0.9647 0.9633 0.8877 30 20 E, kJ mol–1 95% Confidence 142 7 164 8 191 0.13 A, s–1 95% Confidence 8.4 × 104 7.5 × 104 8.8 × 105 8.0 × 105 1.0 × 108 1.5 × 106 r2 0.9722 0.9680 0.9199 *Mean E, kJ mol–1 σ 134 11 160 7 193 2 A, s–1 σ 4.4 × 104 4.1 × 104 5.7 × 105 4.1 × 105 1.0 × 108 0 *Mean values at heating rates of 10, 20, and 30 at a gas flow rate of 20 ml min–1 Table 4. Apparent kinetic parameters for R2, R3, and F1 models at various conditions.
  • 8. RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 8 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg solid-state kinetics. However, if it is not just a math- ematical consequence, the larger range of A values compared to Ea may indicate enhancements at high heating rates largely driven by entropic and much less by enthalpic contributions (KCE was previously known as enthalpy-entropy compensation effect). This means that while the threshold energy transferred though lattice vibrations do not deviate substantially with increased heating rates, the resulting increase in vibratory frequency induces a more efficient release of volatile component. To account for this effect in subsequent model validations and predictions with R models, the mean Ea values were used while A values were adjusted (but maintained within the range obtained) to correspond to the imposed heating rate. As in the case of an isothermal stage, the lowest possible A value within the obtained range (i.e. 1.6 × 105 s–1 for R3’s 5.7 ± 4.1 × 105 s–1 ) was used. The kinetic parameters were validated via recon- structions of the of the DTG curves (obtained using heating rate of 10 °C min–1 ) at the 400–800 °C region. As clearly indicated in Figs 5(a–c), the R3 model provided a good overall match to the experimental measurements. The R3 reconstruction matched well the peak region from 620–800 °C, overall curve shape, −(dm/dt)max and Tp. While during dehydroxylation, minerals may undergo several successive steps, only the R3 mechanism provided a practical, physically evident and phenomenologically valid model for simulating the overall thermal behavior of antigorite. Furthermore, the predictive capability of the R3 model was tested by simulating the effect of sample Figure 5. Model validation via reconstructions of the experimental DTG curve using (a) contracting cylinder R2, (b) contracting sphere R3 and (c) random nucleation model F1. Simulation of DTG curves using the R3 model to predict the effects of (d) sample mass SMx and (e) heating rates HRy.
  • 9. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al. 9© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg Figure 6. Degree of dehydroxylation achieved during heat activation at (a) 730 °C showing the good agreement between experimental and the R3 model prediction (Ea value of 160 kJ mol–1 and A of 5.7 × 105 s–1 for the dynamic heating rate and 1.6 × 105 s–1 for static heating stage, respectively) and (b) experimentally observed activation profile at 630 °C and 730 °C. Lizardite activation at 630 °C is included for comparison. mass and heating rates. Figures 5(d) and 5(e) demonstrated that these effects were well accounted for, showing the increasing trend in the dehydroxyla- tion rates for both process variables, yielding the correct locations of the −(dm/dt)max and Tp. Considering that thermal energy is provided directly from combustion, high-grade heat allows for high temperature operations. Heat activation of antigorite is then best performed at the mineral Tp, where the rate is at its maximum. This heat treatment at 730 °C was then predicted using R3 with Ea of 160 kJ mol–1 antigorite and A of 5.7 × 105 s–1 for heat-up period at 30 °C min–1 and 1.6 × 105 s–1 for the isothermal stage. Figure 6(a) shows the good agreement for the pre- dicted and observed antigorite dehydroxylation carried out at 730 °C. The overall heat treatment process for antigorite, which consists of heat-up and isothermal stages, is complete within 34 min. The heat-up period, from 30 to 730 °C at 30 °C min–1 requires 24 min, while the isothermal stage at 730 °C to attain 90% dehydroxylation adds 6 min to the operation. During the heat-up period, approximately 60% of total hydroxyls were removed from 500–730 °C. Full dehydroxylation requires 10 min of the isothermal operation at 730 °C. But such opera- tion is undesirable, as mineral’s reactivity deteriorates for dehydroxylation in excess of 90%.34 The duration and temperature of dehydroxylation define the reactivity of the activated mineral during dissolution step in the aqueous carbonation. It was observed that ≤ 90% dehydroxylation leads to optimal reactivity.34 Generally, 120 min had been previously used to activate both antigorite and lizardite, with particles −38 μm in size. However, serpentine conversions were significantly higher for antigorite at 92% than lizardite at 40%.11 To probe this difference, we performed isothermal activation at 630 °C for 2 h on the antigorite sample and on another serpentinite containing lizardite as a major phase (both from the Great Serpentinite Belt). Figure 6(b) shows that this heat pre-treatment fully dehy- droxylated lizardite but only removed ~55% of antigorite’s hydroxyl content. Furthermore, the comparison of two activation temperatures for antigorite point up to the differences in dehydroxyla- tion rates at 730 °C and 630 °C. Although the opti- mal degree of dehydroxylation to maximize conver- sion requires experimental verification, the higher conversion for antigorite compared to lizardite may be attributed to the variation in the structural composition of the two minerals. At 40% OH content, only antigorite and dehydroxy- late 1 were present (Table 3). Forsterite only starts to form when OH content is less than 30%. At 90% dehydroxylation, dehydroxylate 2 is visible while both dehydroxylate 1 and antigorite disappear. This occurs at 800 o C, where, as seen from Fig. 4, the interlayer spacings collapse. It can then be deduced that serpen- tine activation must not exceed 90% dehydroxylation to maintain an open, layered structure.
  • 10. RD Balucan et al. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 10 © 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg 3. O’Connor WK, Dahlin DC, Rush GE, Gerdemann SJ and Penner LR, Energy and Economic Considerations for Ex-situ Aqueous Mineral Carbonation, DOE/ARC-2004-028 US Department of Energy, Albany Research Center, Albany, OR, USA (2004). 4. O’Connor WK, Dahlin DC, Rush GE, Gerdemann SJ, Penner LR and Nilsen RP, Aqueous Mineral Carbonation: Mineral Availability, Pre-treatment, Reaction Parametrics, and Process Studies, DOE/ARC-TR-04-002. Albany Research Center, Albany, OR, USA (2005). 5. O’Connor WK, Dahlin DC, Nilsen RP, Rush GE, Walters RP and Turner PC, CO2 storage in solid form: A study of direct mineral carbonation, DOE/ARC-2000-011, in Proceedings of the 5th International Conference on Greenhouse Gas Technologies, August 14–18, 2000, Cairns, Australia (2000). 6. O’Connor WK, Dahlin DC, Nilsen RP and Gerdemann SJ, Continuing studies on direct aqueous mineral carbonation for CO2 sequestration, in Proceedings of the 27th International Technical Conference on Coal Utilization and Fuel Systems, March 4–7, 2002, Clearwater, FL, USA (2002). 7. O’Connor WK, Dahlin DC, Nilsen RP and Turner PC, Carbon dioxide sequestration by direct mineral carbonation with carbonic acid, in Proceedings of the 25th International Technical Conf. on Coal Utilization and Fuel Systems, March 6–9, 2000, Clearwater, FL, USA ( 2000). 8. O’Connor WK, Dahlin DC, Nilsen RP, Rush GE, Walters RP and Turner PC, Carbon dioxide sequestration by direct mineral carbonation: Results from recent studies and current status, in Proceedings of the 1st National Conference on Carbon Sequestration, DOE/ARC-2001-029, May 14–17, 2001, National Energy Technology Laboratory, Department of Energy, Washington DC, USA (2001). 9. Sipilä J, Teir S and Zevenhoven R, Carbon Dioxide Sequestra- tion by Mineral Carbonation - Literature Review Update, Report VT 2008-1.[Online]. Åbo Akademi University, Heat Engineering Laboratory, Turku, Finland, 2008. Available at: http://web.abo.fi/~rzeve nho/MineralCarbonationLiterature Review05-07.pdf [October 21, 2009] 10. IPCC, Special Report on Carbon Capture and Storage, ed by Metz B, Davidson O, de Coninck HC, Loos M, and Meyer LA. Cambridge University Press, Cambridge, UK (2005). 11. Gerdemann SJ, O’Connor WK, Dahlin DC, Penner LR and Rush H, Ex situ aqueous mineral carbonation. Environ Sci Technol 41:2587–2593 (2007). 12. Khoo HH and Tan RBH, Life cycle evaluation of CO2 recovery and mineral sequestration alternatives. Environ Progress 25:208–217 (2006). 13. Zevenhoven R, Fagerlund J and Songkok JK, CO2 mineral sequestration: Developments towards large-scale application. Greenhouse Gas Sci Technol. 1:48–57 (2011). 14. Brent G, Integrated Chemical Process. Patent WO/2008/0631305 A1 (2008). 15. Ball MC and Taylor HFW, The dehydration of chrysotile in air and under hydrothermal conditions. Mineral Mag 33:467–482 (1963). 16. Brindley GW and Hayami R, Kinetics and mechanisms of dehydration and recrystallization of serpentine: I, in Proceed- ings of the 12th National Conference on Clays and Clay Minerals, September 30 – October 2, 1963, Atlanta, GA (1964). 17. Brindley GW, Narahari Achar BN and Sharp JH, Kinetics and mechanism of dehydroxylation processes: II. Temperature Conclusion In this study, we demonstrated the optimization of antigorite heat treatment, providing a benchmark of an extreme case of activation among serpentine minerals. This was made via the development of a novel predictive framework, affording the optimisa- tion of the dehydroxylation process as function of processing temperature and residence time to provide a methodology for designing practical unit operations for thermal processing of serpentinite ores. Based on the observed structural changes, a properly activated antigorite appears to contain between 10 and 40% residual hydroxyls. The optimum activation strategy inferred from the combined kinetic and mechanistic considerations amounts to the production of a 60– 90% dehydroxylated mineral, isothermally at 730 °C for ≤ 6 min. On the other hand, the present results indicate that the reason of low activity of lizardite, reported in literature,11 rests with excessive duration of activation that led to the collapse in the mineral structure and formation of relatively unreactive enstatite upon full dehydroxylation. Generally, the suggested heat treatment strategy translates to a fast and efficient thermal processing in an optimally sized calcining vessel. The activation of the more common serpentine minerals lizardite and chrysotile is ex- pected to be significantly faster as dehydroxylation proceeds at lower temperatures than antigorite. Due to mineralogical differences and composition of serpentinites, heat treatment and its optimization must be unique for each ore. Acknowledgements This study was funded in part by an internal grant (Ref. No. G0189103) from the University of Newcastle. D. Phelan and J. Zobec (EM-X-ray Unit, University of Newcastle) assisted with SEM, XRF and XRD analy- ses. Discussions with Prof. Erich Kisi, Dr Judy Bailey, and Ms Monica Davis are greatly appreciated. Reydick Balucan thanks the University of Newcastle for the postgraduate research scholarship. References 1. Huijen WJJ and Comans RNJ, Carbon Dioxide Sequestration by Mineral Carbonation. Report No. ECN-C--03-016. ECN (Energy Research Centre of Netherlands), the Netherlands (2003). 2. Huijen WJJ and Comans RNJ, Carbon Dioxide Sequestration by Mineral Carbonation. Report No. ECN-C--05-022. ECN (Energy Research Centre of Netherlands), the Netherlands (2005).
  • 11. Modeling and Analysis: Thermal activation of antigorite for the mineralization of CO2 RD Balucan et al. 11© 2011 Society of Chemical Industry and John Wiley & Sons, Ltd | Greenhouse Gas Sci Technol. 1:1–11 (2011); DOI: 10.1002/ghg and vapor pressure dependence of dehydroxylation of serpentine. Am Mineral 52:1697–1705 (1967). 18. Candela PA, Crummett CD, Earnest DJ, Frank MR and Wylie AG, Low pressure decomposition of chrysotile as a function of time and temperature. Am Mineral 92:1704–1713 (2007). 19. Cataneo A, Gualteri AF and Artioli G, Kinetic study of the dehydration of chrysotile asbestos with temperature by in situ XRPD. Phys Chem Miner 30:177–183 (2003). 20. Llanna-Fúnez LS, Brodie KH, Rutter EH and Arkwright JC, Experimental dehydration kinetics of serpentine using pore volumometry. J Metamorphic Geol 25:423–438 (2007). 21. Inque T, Yoshimi I, Yamada A and Kikegawa T, Time-resolved X-ray diffraction analysis of the experimental dehydration of serpentine at high pressure. Mineral Petrol Sci 104:105–109 (2009). 22. MacKenzie KJD and Meinhold RH, Thermal reactions of chrysotile revisted: A 29Si and 25Mg MAS NMR study. Am Mineral 79:43–50 (1994). 23. Perrillat JP, Daniel I, Koga KT, Reynard B, Cardon H and Crichton WA, Kinetics of antigorite dehydration: A real-time X-ray diffraction study. Earth Planet Sci Lett 236:899–913 (2005). 24. Tyburczy JA and Ahrens T, Dehydration kinetics of shocked serpentine, in Proceedings of the 18th Lunar and Planetary Science Conference, March 16–20, 1987, Houston, TX (1988). 25. Weber JN and Greer RT, Dehydration of serpentine: Heat of reaction and reaction kinetics at PH2O = 1 atm. Am Mineral 50:450–464 (1965). 26. Chizmeshya AVG, McKelvy MJ, Sharma R, Carpenter RW and Bearat H, Density functional theory study of the decomposi- tion of Mg(OH)2: A lamellar dehydroxylation model. Mater Chem Phys 77:416–425 (2002). 27. McKelvy MJ, Chizmeshya AVG, Diefenbacher J, Bearat H and Wolf G, Exploration of the role of heat activation in enhancing serpentine carbon sequestration reactions. Environ Sci Technol 38:6897–6903 (2004). 28. McKelvy MJ, Sharma R and Chizmeshya AVG, Lamellar reaction phenomena: From intercalation to nanomaterials formation. J Phys Chem Solids 67:888–895 (2006). 29. Ferriol M, Gentilhomme A, Cochez M, Oget N and Mieloszynski JL, Thermal degradation of poly(methyl methacrylate) (PMMA): Modelling of DTG and TG curves. Polym Degrad Stabil 79:271–281 (2003). 30. Yang J, Miranda R and Roy C, Using the DTG curve fitting method to determine the apparent kinetic parameters of thermal decomposition of polymers. Polym Degrad Stabil 73:455–461 (2000). 31. Martinez E, The effect of particle size on the thermal properties of serpentine minerals. Am Mineral 46:901–912 (1961). 32. Wicks FJ, Status of the reference X-ray powder-diffraction patterns for the serpentine minerals in the PDF data- base-1997. Powder Diffr 15:42–50 (2000). 33. Viti C, Serpentine minerals discrimination by thermal analysis. Am Mineral 95:631–638 (2010). 34. Li W, Li W, Li B and Bai Z, Electrolysis and heat pre-treatment methods to promote CO2 sequestration by mineral carbon- ation. Chem Eng Res Des 87:210–215 (2009). 35. Butt DP, Lackner KS, Wendt CH, Conzone SD, Kung H, Lu Y and Bremser JK, Kinetics of thermal dehydroxylation and carbonation of magnesium hydroxide. J Am Ceram Soc 79:1892–1898 (1996). Reydick Balucan Reydick D. Balucan is a post-graduate researcher working on mineral carbon- ation at the Priority Research Centre for Energy, University of Newcastle. His focus is in the optimization of direct aqueous mineral carbonation of serpentine minerals. He holds a BSc in Chemistry from Negros Oriental State University (Philippines) and will finish his PhD (Chemical Engineer- ing) by 2012. Eric Kennedy Professor Eric M. Kennedy is the Deputy Director of the Priority Re- search Centre for Energy, The Univer- sity of Newcastle. He holds a BSc (New South Wales) in Pure and Applied Chemistry and a PhD (New South Wales) in Physical Chemistry. His interests include mitigation of ozone-depleting gases as well as CO2 capture and storage. John Mackie Professor John F. Mackie is a conjoint professor in Chemical Engineering at the University of Newcastle. He holds a DSc (Sydney) in Chemistry. He specializes in chemical kinetics, quantum chemistry and high tempera- ture chemistry. He is a member of the Priority Research Centre for Energy, University of Newcastle. Bogdan Dlugogorski Prof. Bogdan Z. Dlugogorski is a Fellow of the Australian Academy of Technological Sciences and Engineer- ing and the Director of the Priority Research Centre for Energy, University of Newcastle. He holds a BSc (Cal- gary) in Chemical Engineering and Geophysics, and an MEng (McGill), a PhD (Montreal) and a DSc (Newcastle). His research interests are in process safety and environment protection, including CO2 storage.