Upload
others
View
13
Download
2
Embed Size (px)
Citation preview
Zeolite Reinforced Autoclave Aerated Concrete (AAC)
Michael W. Grutzeck, Maria DiCola
The Pennsylvania State University, University Park, PA 16802
Abstract
Asbestos reinforced concrete is one of the best cementitious composites ever developed.
Due to the hazardous nature of asbestos fibers however alternates have long been under study.
The technology is straight forward. By introducing a fiber that is in equilibrium with the matrix,
the fiber will coexist with and perhaps even bond to the matrix. This behavior will provide a
degree of toughening of the matrix via mechanisms such as pull out, crack bridging and crack
branching. Unfortunately, unlike asbestos, some fibers are not in equilibrium with the matrix and
they will react and partially/totally disintegrate during curing.
Autoclaved aerated concrete (AAC) is light weight due to its cellular character, but it is
also a rather brittle material that is prone to chipping and breakage. It is a mix of Portland
cement, lime and either Class F fly ash or quartz flour. Its cellular nature is provided by the
reaction of flaked aluminum powder with the caustic mixture soon after mixing and molding.
AAC is steam cured in an autoclave at 180°C for 8-12 hours. In an attempt to toughen AAC it was
proposed to grow a zeolitic phase in situ and contemporaneously with the developing
tobermorite matrix during autoclaving.
It was known that certain zeolites could be synthesized and were stable at 180°C and it
was also known that zeolites could be made from Class F fly ash mixed with NaOH solution. It
was hypothesized that a tougher AAC could be produced by adding NaOH to the mix in order to
encourage the formation of zeolites. This was found to be true, but the foaming process in the
presence of NaOH became daunting. Runs were not reproducible. As an alternative, prereacted
zeolitized fly ash was gradually added to a fly ash AAC mix as a substitute for untreated fly ash
and returns. Samples were mixed and foamed in a conventional fashion. Runs were now
reproducible-rises tended to fill the molds completely and as a result final densities were nearly
the same.
Results reported here show that 40 wt% pretreated Class F fly ash that was partially
zeolitized could be substituted for 40 wt% Class F fly ash/returns in a conventional fly ash AAC
mix and that in doing so the AAC could be toughened by ~ 5%. Although this is not a very large
increase it does suggest that the inclusion of a second phase (zeolite A) that is in equilibrium
with the tobermorite that forms in the matrix can toughen AAC. If it were possible to foam a
mixture containing only NaOH and Class F fly ash in a reproducible fashion these zeolite
containing mixtures may provide both a tougher and a “greener” alternative to conventional AAC.
1. Introduction
Zeolites are a class of minerals known for their wide range of commercial uses. They
come in a variety of shapes and sizes, but micometer sized crystals are the norm. Although
occasional hand sized specimens of zeolites are found, to date it has been impossible to grow
such crystals in the laboratory. Perhaps this limitation on size is due to the process by which
zeolites are made to nucleate and grow in the laboratory; time scales are often compressed.
Synthetic zeolites are normally micrometer sized [1].
Zeolites have a relatively open three-dimensional framework structure. The framework is
based upon interconnected [SiO4]4-
and [AlO4]5-
tetrahedra arranged in such a fashion that the
linked tetrahedra define a limited number of regular polyhedra. The tetrahedra are linked
together at their corners through a common oxygen ion. Because of the charge deficiency caused
by the presence of Al in tetrahedral positions zeolites must contain counterions. These ions are
solvated and are incorporated in the voids and channels that occur in the structure along with
additional water molecules. Imagine for a moment a structure made up of tetrahedrally
coordinated (AlSi)O4 ions each linked to one another in three dimensions by a common oxygen
atom (if you will, by the “bars” in the playground structures we called “monkey bars”) and one can
begin to visualize the internal structure of a zeolite [2].
Zeolites can be synthesized from a range of aluminosilicate materials mixed with caustic
solutions (normally Na and K based). Many zeolites are synthesized in an autoclave at elevated
temperatures. The similarity of zeolite synthesis to autoclaved aerated concrete (AAC)
production is explored here. The fact that both AAC and certain zeolites can be synthesized
under saturated steam pressure in a steam heated autoclave at 180°C led us to believe that in situ
growth of zeolites could possibly be used to increase the fracture toughness of AAC. In fact it
has been demonstrated that zeolites can occur in equilibrium with crystalline calcium silicate
hydrate found in AAC, i.e. 1.1 nm tobermorite [3].
The objective of the current study was to determine whether or not an AAC sample
consisting of tobermorite and zeolite would be tougher than a conventional fly ash based AAC
sample. The chemistry seemed correct and it was well known that small amounts of a second
phase dispersed in a given matrix will toughen the matrix via several mechanisms including
crack bridging and pull out.
2. Background
The process of making an AAC sample is more art than a science. There are strict
protocols that must be followed time after time in order to achieve a semblance of product
consistency. Conventional AAC is made from either Class F fly ash or quartz flour [4-6]. Both
starting materials are fine grained and chemically reactive when mixed with Portland cement,
lime, anhydrite and Al powder [4-6]. Typical recipes are given in Table 1 [7]. Mixes can be
made with or without using returns. The industry uses returns and returns tend to make a better
block, but some scientists and engineers use return free mixtures for laboratory sized samples
because they are easier to formulate. Al powder is added at the last minute of mixing, just prior
to molding. Once added the mix is stirred for another 30 seconds or so and then dumped into a
mold. The mixture is very liquid and literally sloshes around in the mold. Once in the mold two
things start to happen. The Portland cement and lime react with the water. The cement dissolves
and a small amount of hydrate is formed. The lime slakes and produces Ca(OH)2 which also has
the benefit of removing some of the water from the mixture and thickening it slightly. The pH of
the solution rises to ~12 and the Al powder which up until this point has done very little will
begin to react with the now alkaline solution and begin to produce hydrogen gas bubbles. Soon
things are fizzing away and the sample rises to about twice its size. This is the aeration process
that produces the cellular character of AAC. Once the “cake” is finished rising and hardens to the
touch (~1 hour) the sample is cut to size and autoclaved at 180°C for 8-12 hours.
Given the limitations imposed upon us by the existing AAC technology it was our
intention to work with the existing mixing and curing process as much as possible so as to make
new discoveries easily adaptable by an existing AAC facility. Because zeolites are
aluminosilicates our first decision was to work exclusively with Class F fly ash based AAC and
Table 1. Formulation of a Typical Quartz AAC and a Fly Ash AAC (weight %)
Ingredient Quartz AAC (wt%) Fly Ash AAC (wt%)
with returns* w/o returns with returns w/o returns
Quartz Flour 25.4 34.7 -- --
Dry Class F Fly Ash -- -- 41.1 41.7
Dry Returns 10.0 -- 9.0 --
Portland Cement 14.0 14.7 10.2 19.7
Quick lime 9.0 9.4 3.5 4.8
Al flake 0.05 0.04 0.04 0.07
Anhydrite/gypsum 1.8 (G) 1.8 (G) 1.7 (A) 1.7 (A)
Water 39.8 39.4 34.5 32.1 *Returns are the recycled unautoclaved trimmings that the AAC industry uses as one of their raw materials.
begin to add NaOH to the basic mix to see if it was possible to grow zeolites in situ within the
normal tobermorite containing matrix. It was known that it was possible to mix Class F fly ash
with NaOH to produce zeolites [8-23]. It was also known that it was possible to blend Portland
cement with fly ash and NaOH and cure it at 185°C to achieve a phase assemblage containing
tobermorite and zeolite [3,24], but because of the caustic nature of the NaOH, it was in fact
impossible to foam the material in any fashion that was close to reproducible. The NaOH caused
the mix to foam in the mixer-which is not good. After trying oxidized Al powder, coarser grained
powders, chemical foams and the like this effort was abandoned. However, during the one year
spent on this task and some 150 trial mixtures information was gained on the phase chemistry
and behavior of these materials as a function of bulk density.
Using this information it was then decided to make a series of five samples using
prereacted fly ash, fly ash that had been reacted with ~2M NaOH solution in a 5 gallon
continually stirred bucket at 90°C for 3 days. The resulting partially converted slurry had a pH
near 10 and this seemed to indicate that the reaction had gone as far as it could. The slurry was
air dried at 38°C and then used as a partial to complete substitute for Class F ash and “returns” used
in the AAC making process. See Figure 1 later. Returns are the trimmings from the green cake
that is removed from the cake as it is trimmed and cut to size before autoclaving. Now it was
possible to keep conditions relatively unchanged – we did not add NaOH during mixing and thus
the Al powder reacted in a normal fashion. This allowed us to produce a Control Sample
consisting of 100 % fly ash and returns and companion samples containing 25 %, 50%, 75% and
100% zeolite substituted for the fly ash and returns. See recipes given in Table 2. It was found
that the zeolites were often consumed by the reaction of lime with the added zeolite to produce
tobermorite, but that on occasion they survived and continued to co-exist with tobermorite that
formed. These data are presented here. There is a suggestion that small quantities of zeolites (up
to 40 wt% substitution for fly ash and returns) add strength and toughness to a conventional
AAC block. This is a possible means of addressing toughness issues. Durability of the composite
block is under study. Zeolites could well lend freeze thaw resistance to the block because the
zeolites have large amounts of internal space that might be able to accommodate expansion.
3. Experimental Methods
Samples were mixed in a large laboratory sized Warring blender capable of holding 6
liters of liquid. Class F fly from Allegheny Energy’s Ft. Martin power plant was used as the major
ingredient. It was used as received or in a partially zeolitized state. The fly ash/zeolite was mixed
with vertical kiln lime from Mississippi Lime, Type I Portland cement from Medusa now known
as Cemex, anhydrite from U.S. Gypsum and Al powder from MD-Both Industries. Returns were
prepared from the same mixtures made without returns. After the mix had expanded and become
hard at 38°C, it was pulverized and dried. This became the source of returns. Returns are used by
the industry to incorporate green cake trimmings and waste. It has been found that including
returns in the AAC mix produces a better performing block. Once again see Table 2 for the
recipes used to make the 5 mixtures that were studied.
Table 2. Recipes used to make a mix that would expand and fill the mold to slightly overflowing. Weights in
grams. Figures in parentheses are wt% of total mix.
sample water Class F
fly ash
returns zeolite Portland
cement
anhydrite Miss.
lime
Al-
powder
control 2350
(34)
2800
(41)
613
(9)
0 695
(10)
116
(2)
238
(3)
3.3
(0.05)
25 zeolite 2415
(35)
2100
(30)
460
(7)
853
(12)
695
(10)
116
(2)
238
(3)
3.3
(0.05)
50 zeolite 2481
(36)
1400
(20)
307
(4)
1707
(25)
695
(10)
116
(2)
238
(3)
3.3
(0.05)
75 zeolite 2546
(36)
700
(10)
153
(2)
2560
(37)
695
(10)
116
(2)
238
(3)
3.3
(0.05)
100 zeolite 2612
(37)
0 0 3413
(48)
695
(10)
116
(2)
238
(3)
3.3
(0.05)
The ingredients were combined as follows. The liquid (hot tap water) was placed in the
blender and the returns were added to it and blended for the few minutes or so needed to weigh
out the fly ash/zeolites. These were then added to the blender and blended for 5 minutes or so
needed to finish weighing the other ingredients. Speed was adjusted with a rheostat to achieve a
vortex in the mixer. The Portland cement was added next and allowed to blend for 3 minutes.
The anhydrite was added next followed closely by the lime. The lime is a slow slaking vertical
kiln lime that slakes in 3-6 minutes. It was added and blended for 1 minute followed by the Al
powder dispersed in a little water. The entire mix was blended for 15 seconds and then poured
into oil coated 4x4x25 inch bar molds kept in a 38°C walk in curing chamber. The bars were
covered with a plastic tent and allowed to rise/cure overnight. They were then demolded and
autoclave cured at 180°C for 12 hours. After curing, the bars were cut to final size on a bandsaw,
notched at their midpoints to ~1/4 inch deep and tested for their toughness using a 3-point bend
test. The broken arms of the bars were cut into 4-inch cubes and tested for compressive strength.
Smaller samples were dried at 70°C to constant weight and their densities were calculated. SEM
and X-ray analyses were also carried out using a Hatachi S 3000 H SEM and a Sintag X-ray Cukα
diffractometer running at 2-4° per minute.
4. Results
A summary of dry density, compressive strength, bending MOR and fracture toughness
data for the 5 mixtures studied is given in Table 3. Bending MOR and fracture toughness were
measured using 4 x 4 x 27 inch bars of AAC that were notched (~ 0.5 inches) at their mid points
using a band saw. The method is similar to that used by Whittman and Gheorghita [25] to
measure fracture toughness. The bar was loaded as in a three point bend test which had the effect
of opening the preexisting crack. Toughness was calculated by measuring the area under the
stress-strain curve. An SEM image of the zeolitic fly ash is given in Figure 1, Figures 2-6
represent the microstructures of the zeolite substituted AAC samples, and Figure 7 provides
insight into how well the added zeolites survive the autoclaving process. The peaks present in the
X-ray pattern represent the phases in the AAC samples. Zeolite and tobermorite peaks tend to
grow in intensity as more zeolite is substituted for fly ash/returns. This suggests that crystallinity
of the sample is increasing, which is in fact also reflected in the accompanying SEM images.
Table 3. Dry density, compressive strength, MOR and fracture toughness of zeolite containing AAC samples.
sample Dry density
(Kg/m3)
Compressive
strength (MPa)
Bending MOR
apparent (MPa)
Fracture toughness
(KN/m3/2
)
Control 638 ± 13 4.85 ± 0.70 σ 0.527 ± 0.001 σ 0.1047 ± 0.0006 σ
25 zeolite 608 ± 19 4.23 ± 0.53 σ 0.613 ± 0.024 σ 0.1194 ± 0.0037 σ
50 zeolite 596 ± 14 3.35 ± 0.22 σ 0.590 ± 0.012 σ 0.1164 ± 0.0019 σ
75 zeolite 603 ± 5 2.74 ± 0.12 σ 0.424 ± 0.030 σ 0.0809 ± 0.0043 σ
100 zeolite 601 ± 11 1.97 ±0.09 σ 0.323 ± 0.007 σ 0.0652 ± 0.0004 σ
Figure 1. This is a micrograph of our prereacted fly
ash showing the extent of the zeolite overgrowths that
were produced during continual mixing of the fly ash
in a 2 M NaOH solution at 90°C for 3 days. It is
interesting to speculate as to the reactivity of these
grains with Portland cement/lime. A priori, it would
seem that the very fine grained zeolite crystals that
make up the overgrowth around unaltered glass cores
would be more reactive than the glass. Zeolites are a
proven pozzolan. For this reason it is expected that the
Na-Al-Si in the zeolite would combine with the lime in
the mix to produce tobermorite. This would expel Na
and Al which would in turn form hydrogarnet and a
rather caustic solution. The caustic could then react
with the glassy cores to produce more zeolites.
Figure 2. Control sample made without zeolite additive. Matrix is dense with some porosity. Open spaces are
being bridged by needle shaped crystals. The crystal development in the bubble is not that striking. The
particles that are present are covered with a film of extremely small fibrous crystals. The overall impression
is one of a “gel-like” appearance with crystal growth occurring on the surface of the gel..
Microstructure
The microstructure of the suite of samples is not as telling as one might expect. The basic
macro structure of AAC (hand specimen) consists of mm sized gas bubbles dispersed in a matrix
of some kind. In Figure 2-6 we reproduce a set of 5 photomicrographs that are as representative
as possible taken at equivalent original magnifications. What we show for each figure is a low
magnification overview of the appearance of a broken surface of the matrix material between
bubbles (1,000X on the left), and a much higher magnification of the crystal development in a
bubble (5,000X on the right). It has been observed that the inside of bubbles allow crystals to
grow into empty space and develop their crystalline structure to the fullest extent. Figure 2
represents the Control sample and Figure 6 represents the equivalent sample made with 100%
zeolite. The other figures represent the samples in between these end members.
Figure 3. Control sample with 25 wt% zeolite substituted for flay ash. The matrix looks dense with little if
any open spaces. There are spherical shapes present but few broken spheres (fly ash remnants). It looks as if
spheres are pulled out (plucked from the matrix whole) rather than breaking during the sample preparation
process. The crystal development within a bubble is very striking. There is a sense that the rounded shapes
are now covered with these intricate “balls of yarn” looking crystals.
Figure 4. Control with 50 wt% zeolite substitution for fly ash. The morphology of the 50:50 sample is also
dense but perhaps there is a bit more porosity. There is little spherical character left. Particles seem to be
more angular and well meshed together. There are some small needle shaped crystals present here and there
bridging gaps but this is not as common as in other samples.The bubble morphology once again has a gel-like
appearance, much like Figure 2. Crystals seem to grow out of the gel layer and link the particles together.
X-ray Diffraction Patterns
X-ray diffraction patterns are provided as a means of gauging how the zeolite
substitutions fare when mixed with Portland cement, AAC returns, lime and anhydrite. The
series represents a complete substitution of 3400 grams of a blend of 82 % Class F fly ash and 18
% returns by weight by our pretreated zeolite containing fly ash in four 25% steps. The trace at
the bottom of Figure 7 represents the control sample that contains no zeolites at all. The
Figure 5. 75 wt% Zeolite substitution for fly ash has the affect of reintroducing a spherical feel to the
morphology. Rounded particles seem to abound, some are covered fine crystals whereas others are smooth.
The latter situation suggesting that a covering was pulled away during sample preparation. The sapmle
appears to have porosity associated with the more spherical particles, they do not seem to be lined together as
well as other samples. The morphology development in the bubble indicates that two phases are present: the
ball of yarn crystals and some very smooth rounded particles. These could be glass remnants during
dissolution of a larger fly ash particle or the nucleus of growing zeolite crystals.
Figure 6. 100 wt% Substitution of zeolite for fly ash causes the sample to develop a noticeable “fuzzy”
appearance. The sample matrix consists of lots of spheres of fly ash covered with very fine crystals. Some of
the fly ash spheres have broken during sample preparation exposing scoratious glass cores. Particles seem to
have open pore spaces around them. The structure in the bubble again shows two phases. In this case the
fibers are straighter and better at filling spaces between the grains. Also present is the second phase
consisting of smooth crystalline shapes.
uppermost trace contains all zeolite and no flyash or returns. One is able to see a gradual change
in crystallinity with the addition of our Na-zeolites. As might be expected, the peaks for Na-P1
(N) increase as we add more Na-P1 to the system. Unexpectedly however the crystallinity of the
tobermorite (T) also increases. Mullite (M) and quartz (Q) are present in the fly ash. These tend
to remain reasonably constant. Some calcium carbonate (CC) and katoite (K) are also present in
all of the samples. Katoite and tobermorite are normally found in conventional fly ash based
AAC. The association of zeolite and tobermorite in the Na-zeolite containing AAC is a new
finding. There is a definite change in phases that are stable with one another occurring as we
move from one end member to the other.
Figure 7. X-ray diffraction patterns for zeolite substituted AAC samples. T=tobermorite, N=Na-P1,
K=katoite, M=mullite, Q= quartz, CC=calcium carbonate
5. Discussion
As is common when reporting AAC data, the data are often plotted as a function of dry
density. This serves the purpose of taking differences in density into account. For it is well
known that less dense AAC samples are not as strong as denser ones. In the current case however
formulation design tended to produce samples having approximately the same densities. See
Figure 8 – blue plot. The measured dry densities decrease slightly as one begins to substitute
zeolitic fly ash for raw fly ash+returns but then it levels off at ~ 0.6 g/cc for the next 4 mixtures.
It is a small drop, but one that might be anticipated in as much as rise volumes were kept
relatively constant and the fact that zeolite densities are lower than fly ash (for example window
glass = 2.5, zeolite = 2.0). Unlike density however there is a near linear decrease in strength with
increasing percentage of zeolite added (pink plot), values drop from ~ 5 MPa to 2 MPa. This was
unexpected. The SEM microstructures of these samples suggest that the more zeolite rich
samples were more crystalline, i.e. they contained a greater proportion of tobermorite and zeolite
Na-P1 than the control sample. Why a greater amount of crystallinity should reduce strength
remains puzzling. More gratifying was the fact that ~40 percent substitution of zeolite in the mix
resulted in a marked increase in bending strength and fracture toughness (light blue and yellow,
respectively). The SEM images suggest that the relatively blocky zeolite crystals might be acting
as barriers to cracking-perhaps causing crack bridging to occur.
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0 0.2 0.4 0.6 0.8 1 1.2
PERCENT ZEOLITE SUBSTITUTED IN AAC
DE
NS
ITY
(g
/cc),
CO
MP
RE
SS
IVE
ST
RE
NG
TH
(M
Pa x
10-1
), M
OR
(MP
a),
FR
AC
TU
RE
TO
UG
HN
ES
S
(kN
/m3/2
)
Figure 8. Plot of density ( g/cc blue), compressive strength (MPa /10 pink), MOR (MPa light blue) and
fracture toughness ( kN/m3/2
yellow) as a function of the percentage of zeolitic fly ash used in preparing the
mixture.
6. Conclusions
It is concluded that zeolites can be added to a Class F fly ash AAC mixture as a partial
replacement for raw fly ash/returns. Toughness and bending MOR rise slightly up to and reach a
maximum value at ~ 40 wt% zeolite additions. Beyond this crystallinity increases but toughness
and MOR fall off. Thus it is concluded that a small substitution of zeolite will increase
performance, but the increase is rather small considering the effort needed to achieve it. If
however one looks to other possible uses for such a material one can begin to envision how a
zeolite panel might be able to interact with the environment if placed inside an office building.
Such a panel could possibly adsorb moisture, organics and perhaps even deactivate bacteria and
viruses. These composites could be one of the so called “smart building materials.” As a new
building material a zeolite containing AAC could well provide a different level of protection than
conventional lime-silica building materials.
7. References Cited
1. Breck, D.W., Zeolite Molecular Sieves, John Wiley and Sons, New York (1974).
2. Barrer, R.M., Zeolites and Clay Minerals as Sorbents and Molecular Sieves, Academic Press,
London (1978).
3. Grutzeck, M., S. Kwan and M. DiCola, “Zeolite formation in Alkali-Activated Cementitious
Systems,” Cem. Concr. Res. 34, 949-955 (2004).
4 Autoclaved Aerated Concrete, Moisture and Properties, Developments in Civil Engineering,
Vol. 6, F.H.Wittmann, Ed., 380 pp., Elsevier Publishing Co., Amsterdam (1983).
5. Advances in Autoclaved Aerated Concrete, Proc. 3rd RILEM Inter. Symp. Aerated
Autoclaved Concrete, F.H. Wittmann, Ed., 364 pp., Publishing Co., Amsterdam (1992).
6. Autoclaved Aerated Concrete, Properties, Testing and Design, RILEM Recommended
Practice, RILEM Tech. Committee 78-MCA and 51-ALC, F.H. Wittmann, Ed., 404 pp.,
E&FN Spon, London (1993).
7. Grutzeck, M.W., “Cellular Concrete,” pp. 193-223 in Cellular Ceramics: Structure,
Manufacturing, Properties and Applications, M. Scheffler and P. Colombo (Eds.), Wiley-
VCH, Weinheim (2005).
8. Henmi, T., "Synthesis of Hydroxy-Sodalite ("Zeolite") from Waste Coal Ash," Soil Sci. Plant
Nutr. 33, 517-521 (1987).
9. Mondragon, F., F. Rincon, L . Sierra, J. Escobar, J. Ramirez and J. Fernandez, "New
Perspectives for Coal Ash Utilization: Synthesis of Zeolitic Materials," Fuel 69, 263-266
(1990).
10. LaRosa, J., S. Kwan and M.W. Grutzeck, "Zeolite Formation in Class F Fly Ash Blended
Cement Pastes," J. Amer. Ceram. Scoc. 75, 1574-80 (1992).
11. LaRosa, J., S. Kwan and M.W. Grutzeck, "Self-Generating Zeolite Cement Composites," in
Mat. Res. Soc. Symp. Proc. Vol. 245, 211-216, Mat. Res. Soc, Pittsburgh (1991).
12. Shigemoto, N., K. Shirakami, S. Hirano and H. Hayashi, "Preparation and Characterization
of Zeolites from Coal Ash," Nipp'on Kagaku Kaishi 1992, 484-92 (1992).
13. Shigemoto, N., H. Hayashi and K. Miyaura, "Selective formation of Na-X Zeolite from Coal
Fly Ash by Fusion with Sodium Hydroxide prior to Hydrothermal Reaction," J. Mat. Sci.28,
4781-86 (1993).
14. Chang, H.-L. and W.-H. Shih, "Conversion of Fly Ashes to Zeolites for Waste Treatment,"
Environmental Issues and Waste Management Technologies, V. Jain and R. Palmer, Eds.,
Ceramic Transactions, Vol. 6l, 81-88 (1995).
15. Lin, C-.F. and H.-C. Hsi, "Resource Recovery of Waste Fly Ash: Synthesis of Zeolite-like
Materials," Environ. Sci. Tech. 29, 1109-17 (1995).
16. Park, M. and J. Choi, "Synthesis of Phillipsite from Fly Ash," Clay Sci. 9, 219-229 (1995).
17. Querol, X., A. Alastuey, J.L. Fernandez-Turiel and A. Loez-Soler, "Synthesis of Zeolites by
Alkaline Activation of Ferro-Aluminous Fly Ash," Fuel 74, 1226-31 (1995).
18. Shigemoto, N., S. Sugiyama, H. Hayashi and K. Miyaura, "Characteristics of NaX, Na-A,
and Coal Fly Ash Zeolites and their Amorphous Precursors by IR, MAS NMR and XPS," J.
Mat. Sci.30, 5777-83 (1995).
19. Shih, W.-H., H.-L. Chang, and Z. Shen, "Conversion of Class-F Fly Ash into Zeolites," in
Mat. Res. Soc. Symp. Proc. Vol. 371, pp 39-44 (1995).
20. Singer, A. and V. Berkgatit, “Cation Exchange Properties of Hydrothermally Treated Coal Fly
Ash," Environ. Sci. Technol. 29, 748-53 (1995).
21. Amrhein C., G.H. Haghnia, T.S. Kim, P.A. Mosher, R.C. Gagaiena, T. Amanios and L. de La
Torre, "Synthesis and Properties of Zeolites from- Coal Fly Ash", Environ. Sci. Tech. 30,
735 (1996).
22. Suyama, Y., K. Katayama and M. Meguro, "NH4+-Adsorption Characteristics of Zeolites
Synthesized from Fly Ash," Chem. Soc. Japan 1996, 136-40 (1996).
23. Querol, X, A. Alastuey, A. Lopez-Soler, F. Plana, J.M. Andres, R. Juan, P. Ferrer and C.R.
Ruiz, "A Fast Method for Recycling Fly Ash: Microwave-Assisted Zeolite Synthesis,"
Environ. Sci. Tech. 31, 2527-13 (1997).
24. Grutzeck, M.W., S. Kwan and M. DiCola, “Alkali Activated Autoclaved Aerated Concrete
made with Fly Ash Derived Cenospheres: Effect of Fly Ash and Precuring Temperature, in
11th
International Congress on the Chemistry of Cement, Durban, South Africa 11-15 May
2003.Cement Concrete Institute, Durban (2003).
25. Whittman,F.H. and I. Gheorghita, “Fracture Toughness of Autoclaved Aerated Concrete,”
Cem. Concr. Res. 14, 369-374 (1984).