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International Journal of Engineering Research and Development
e-ISSN: 2278-067X, p-ISSN: 2278-800X, www.ijerd.com
Volume 11, Issue 04 (April 2015), PP.60-66
60
Dealumination and Na activation of natural zeolite for CO2
adsorption on biogas
Aldrin D. Calderon1,2
, Blessie A. Basilia1,2
, Araceli M. Monsada1
,
Edmar P. Casa1
, Lumen C. Milo1
, Marianito T. Margarito1
1
Industrial Technology Development Institute, Department of Science and Technology, DOST Compound,
Bicutan, Taguig City, Philippines
2
School of Graduate Studies, Mapua Institute of Technology, Intramuros Manila, Philippines
Abstract:- In this study, natural zeolites from the Philippines were modified using NaOH heat treatment and
NaCl hydrothermal process. Pre-treatment using ferro-filtering and dealumination using different concentrations
of HCl acid leaching were prepared prior to sodium activation. Heat treatment was performed using 5M NaOH
at 80 °C for 72 hrs while 3 cycle hydrothermal process was performed using 5M NaCl at 10 psi for 1 hr.
Diffraction pattern from XRD showed Heulandite (HEU) – Clinoptilolite (CLI) and Mordenite (MOR)
framework for raw and acid pre-treated zeolites. There was a shift in HEU characteristic peak from 9.9084° and
8.91 Å to 9.6901° and 9.12 Å which can be attributed to the decrease of contribution of HEU type zeolite. The
decrease in contribution enabled the peak to move towards 9.10 Å, value expected for MOR. However, it was
found that presence of amorphous phase widens MOR structure on d-spacing 13.45 Å that created humps.
Reduction of intensity peaks on HEU – CLI on 9.85°, 9.88° and 22.22° regions were observed attributed to acid
leaching. The decline on this characteristic peaks implies severe degradation of crystal framework after heavy
acid treatment although the framework was stable. Acid treated modified zeolites intensify Si/Al ratio due to
dealumination. Sodium uptake along with higher Si/Al ratio was preferred for CO2 adsorption in a mixed gas
system of CO2/CH4. Both NaOH heat treatment and NaCl hydrothermal process increase Na uptake as
confirmed by EDS but the latter is preferred due to higher Si/Al ratio..
Keywords:- Dealumination, Na activation, Zeolite, Si/Al ratio, CO2 adsorption
I. INTRODUCTION
Natural and synthetic zeolites are long been used in various industrial applications [1-10]. Zeolite is a
crystalline aluminosilicate with a three-dimensional framework structure that forms uniformly sized pores,
channels and cavities of molecular dimensions [11]. Zeolite is made of negatively charged alumino-silicate
building blocks that are stabilized by cations such as calcium and sodium [12-20]. Different classifications of
zeolites exists, as a general rule, it is grouped in different frameworks based on the arrangement of T-atoms [21].
The structure of zeolites contains aluminum, silicon, and oxygen in regular frameworks with cations and water
in the pores.
Zeolites as the physical adsorbents for CO2 capture have been reviewed and explored by numerous
researchers [22-26]. Since the gas adsorption reactions initially take place at the surfaces, the elements at the
surface play an important role in the initial adsorption process [27-28]. Literatures on zeolite and its preparation
with synthesis and modifications have been widely published to improve the adsorption characteristics of
zeolites [29-34].
Hydrothermal treatment of zeolites involves the application of high pressure to effectively exchange
native calcium cations into sodium [35-37]. This process is widely used to produce high quality modified
zeolites. In this study, hydrothermal treatment was used and compared to reflux heat treatment and effects of
acid pre-treatment. To date, limited published articles are seen on engineered Philippine natural zeolites.
II. METHODOLOGY
Natural local zeolites were acquired from Industrial Technology Development Institute under the
Department of Science and Technology, Government of the Philippines, thru the Materials Science Division.
These zeolites were prepared by continuous washing and passing thru a magnetic separator for ferro-filtering to
remove ferrous substance then air-dried at 25 °C for 1 week. Effective separation of zeolite and fine iron
particles from slurries passing by gravity flow is needed prior to modification since natural zeolites have high
iron content embedded into their cavities which move into extra framework of zeolites upon high temperature
calcination or steaming. Three (3) bags of 300 grams each were used for acid pre-treatment using hydrochloric
acid with different molarity of 0M, 1M, 3M and 5M of HCl respectively that lasted for 48 hours at 25 °C. These
Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas
61
acid pre-treated zeolites were washed using distilled water until pH is equal to 7. Upon washing, acid pre-treated
zeolites were dried at 80 °C for 72 hours. Dried acid-treated zeolites were manually crushed and pounded until it
passed thru Tyler mesh no. 100. Particle sizes were below 149 microns prior to sodium activation. There were
three conditions considered in the sodium activation of zeolites. First condition was the heat-treatment process
where acid pre-treated zeolites underwent NaOH reflux for 72 hours at 80 °C hot plate. Second condition was
the hydrothermal condition where raw and acid pre-treated zeolites with 5M NaOH were subjected to a 3 cycle
pressurized cooker of 10 psi for 1 hour. Third condition was 3 cycle hydrothermal modification using 1M and
5M NaCl for 1 hour in a pressure cooker of 10 psi.
About 30 grams of 1M, 3M and 5M HCl acid pre-treated zeolites were subjected to 3M and 5M NaOH
heat-treatment for 72 hours at 80 °C. Also, about 30 grams each of 3M and 5M HCl pre-treated zeolite were
prepared for a 3 cycle 5M NaOH hydrothermal process where 10 psi for 1 hr process time is used each cycle.
Washed until pH was equal to 7 and dried for 72 hrs at 80 °C, modified zeolites were pounded until particle
sizes of less than 149 microns were acquired using Tyler mesh no. 100.
Hydrothermal synthesis was performed after preparation of 1M and 5M NaCl in a beaker over 400 rpm
magnetic stirrer for 2 hrs. About 20 grams of acid treated zeolites were mixed in autoclave bottles with 200 mL
of 1M and 5M of NaCl separately in a pressure cooker of 10 psi for 1 hr. After 3 cycle hydrothermal
modification, zeolite were washed until pH was equal to 7 and then dried for 72 hrs at 80 °C.
III. RESULTS AND DISCUSSIONS
Elemental spectra were acquired using Energy dispersive x-ray spectrometer (EDS) by Oxford
Instruments attached to the Nano Helios Focused Ion Beam – Field Emission Scanning Electron Microscopy
(FIB-FESEM) by FEI. Using less than 4 mm working distance and 20 – 25 kV beam voltage, spectra and
mapping were captured to evaluate elemental composition of each acid pre-treated zeolite as presented in Fig. 1.
EDS was used to acquire elemental composition of different types of zeolites. Using Helios FIB-FESEM
coupled with EDS, elemental spectra were acquired and studied. Summary of elemental data for different treated
zeolite from pre-treatment HCl acid pre-treatment, NaOH heat treatment, and NaCl hydrothermal process were
presented in Fig. 2 and 3 showing elemental composition and Si/Al ratio respectively.
Fig. 1 EDS complete elemental data mapping of acid pre-treatment for: (a) raw zeolite,
(b) 1M HCl pre-treatment, (c) 3M HCl pre-treatment, (d) 5M HCl pre-treatment
Using SHIMADZU X-Ray diffractometer LAB X, crystal structures of raw and treated zeolites were
studied. Dried zeolite powdered samples about 3 μm thick were mounted in the XRD sample holder. The
diffractometer model XRD-6000 using Cu K-alpha target was running at 40 kV and 30 mA. At a continuous
scan mode and rate of 1 deg/min, scan range from 2 – 60° were evaluated using divergence slit of 1°, scattering
slit of 1°, and receiving slit of 0.3 mm at 0.01° sampling pitch. Pre-treated zeolite using HCl were subjected to
XRD for elemental analysis. Heulandite (HEU) – Clinoptilolite (CLI) and Mordenite (MOR) framework were
(a) (b)
(c) (d)
Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas
62
detected based on diffractograms of ferro-filtered zeolite and different acid pre-treated zeolites as shown in
different XRD patterns.
After 1M and 5M NaCl hydrothermal synthesis was performed for 0M, 1M, 3M and 5M HCl pre-
treated zeolites, samples were washed until pH was equal to 7 and then dried for 72 hours at 80 °C. Dried
samples about 3 μm thick were mounted in the XRD sample holder where crystal structures were studied as well.
0 5 10 15 20 25 30 35 40 45 50 55 60 65
0
1000
2000
3000
4000
MOR
2.795
HEU
HEU
MOR
MOR
MOR
3.180
2.967
13.475 3.397
3.461
3.952
8.920
I(counts)
2THETA (deg)
FERRO-FILTERED ZEOLITES
0 5 10 15 20 25 30 35 40 45 50 55 60 65
0
1000
2000
3000
4000
MOR
FF + 1M HCl ACID TREATED
HEU
3.960
I(counts)
2THETA (deg)
MOR
13.556
HEU
8.954
MOR
3.468
3.397
MOR
3.178
2.8132.971
1.993
0 5 10 15 20 25 30 35 40 45 50 55 60 65
0
1000
2000
3000
4000
MOR
1.994
FF + 3M HCl ACID TREATED
I(counts)
2THETA (deg)
MOR
8.985
HEU
7.570
HEU
3.969
MOR
3.467
3.0002.818
0 5 10 15 20 25 30 35 40 45 50 55 60 65
0
1000
2000
3000
4000
MOR
FF + 5M HCl ACID TREATED
1.998
2.827
MOR
I(counts)
2THETA (deg)
9.120
HEU
3.988
HEU
MOR
3.480
Fig. 2 Diffractogram of different concentration of acid pre-treatment for: (a) raw zeolite,
(b) 1M HCl pre-treatment, (c) 3M HCl pre-treatment, (d) 5M HCl pre-treatment
0 5 10 15 20 25 30 35 40 45 50 55 60
0
1000
2000
3000
4000
5000
6000
SOD
2.095
SOD
2.554
SOD
2.798
SOD
3.612
I(counts)
2 THETA (deg)
FF + 0M HCl + 5M NaOH
FF + 1M HCl + 5M NaOH
FF + 3M HCl + 5M NaOH
FF + 5M HCl + 5M NaOH
5M NaOH HEAT TREATMENT PROCESS
SOD
6.256
0 5 10 15 20 25 30 35 40 45 50 55 60
0
1000
2000
3000
4000
5000
6000
I(counts)
2 THETA (deg)
FF + 5M HCl + 5M NaCl
FF + 3M HCl + 5M NaCl
FF + 1M HCl + 5M NaCl
FF + 0M HCl + 5M NaCl
FF + 5M HCl + 1M NaCl
FF + 3M HCl + 1M NaCl
FF + 0M HCl + 1M NaCl
RAW
1M and 5M NaCl HYDROTHERMAL PROCESS
Fig. 3 Diffractograms of modified zeolites
(a) (b)
(c) (d)
Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas
63
Fig. 4 Cone bar graph of elemental composition of zeolites
Fig. 5 Cone bar graph of Si/Al Ratio for different types of zeolite processing
Diffraction pattern from XRD showed Heulandite (HEU) – Clinoptilolite (CLI) and Mordenite (MOR)
framework for raw and acid pre-treated zeolites. Upon HCl acid pre-treatment, same structure were acquired.
There was a shift in HEU characteristic peak from 9.9084° and 8.91 Å to 9.6901° and 9.12 Å which can be
attributed to the decrease of contribution of HEU type zeolite. The decrease in contribution enabled the peak to
move towards 9.10 Å, value expected for MOR. However, it was found that presence of amorphous phase
widens MOR structure on d-spacing 13.45 Å that created humps.
Also, reduction of intensity peaks on HEU – CLI on 9.85°, 9.88° and 22.22° regions were observed
attributed to acid leaching. The decline on this characteristic peaks implies severe degradation of crystal
framework after heavy acid treatment. Meanwhile, heat treatment using 5M NaOH showed different zeolite
framework compared to raw and other modification. Comparison of interplanar spacing (d-spacing) and relative
intensities similar to Kotashane et al. in 1986 proves an effective approach in defining zeolite frameworks.
Characteristic peaks with diffraction pattern revealed sodalite octahydrate (SOD) type zeolite for 5M NaOH
heat treatment modification, same structure formed by Baccouche et al. in 1998 for preparing sodalite
octahydrate from 5M NaOH. A sodalite octahydrate framework was produced with literature value of window
pore size 0.27 nm which is applicable for water separation. In general, zeolites with low Si/Al ratio (Si/Al < 5),
Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas
64
for example, zeolites A (LTA), X (FAU), and hydroxysodalite (SOD), are prepared from reaction mixtures with
low Si/Al ratio and strong alkalinity. Sodalite has been theoretically suitable for hydrogen storage, water
selective material and H2/CH4 separation because of low Si/Al ratio. Produced sodalite is an assembly of β-
cages, the building blocks of many other zeolites which could be used for future study. The increase of
alkalinity affects the induction and nucleation periods and speed up the crystallization of zeolites, forming new
framework.
The Si/Al ratio in the reaction system plays an important role in determining the structure and
composition of the crystallized product. Alkaline solution contributes in dispersing the Si/Al ratio (T-atoms)
during growth. Meanwhile, the effects of higher NaCl concentration on hydrothermal modification were seen in
stacked pattern diffractogram of 1M and 5M NaCl. In 5M NaCl hydrothermal process, peak height significantly
increases compared to 1M NaCl owing to higher intensity counts. Although strongest peaks did not alter much,
reduction in characteristic HEU peaks was expected during hydrothermal process at 10 psi due to the severe
pressure experienced by zeolite. With minimal shifts on MOR diffraction peaks for both acid pre-treatment and
hydrothermal processes, MOR phase was far more resistant to chemical and thermal treatment than HEU type.
The interferences of predominant peaks of other crystalline phase lead to minimal peak shifting but slight
shrinking of zeolite cells.
IV. CONCLUSIONS
Sodium activation was successfully performed using heat treatment and hydrothermal treatment. Both
NaCl hydrothermal process and NaOH heat treatment increase Na content of modified zeolites based on EDS
spectra. Too much sodium and basic in nature, NaOH treated zeolites transformed into a new framework of
sodalite type as confirmed by XRD peaks. Sodium as major cation present in modified zeolites performs the
higher CO2 adsorption capacity compared to lower sodium but molecular sieving would be eliminated in the
transport mechanism if sodalite type zeolite would be used for CO2/CH4 gas separation. In terms of sodium
composition of zeolite and higher Si/Al ratio, NaCl hydrothermal process was preferred for CO2/CH4 gas
separation experiment although sodium acquired during NaCl hydrothermal process was far less active than the
NaOH heat treatment process. Moreover, dealuminated zeolite reduces the acidity of zeolite surface which is
preferred since the zeolite must have basic surface in order for the CO2, as Lewis acid, to act on zeolite base
sites. CO2 adsorption would be more effective in a basic surface of zeolite with higher Si/Al ratio for the
adsorption of non-polar compounds such as CO2.
ACKNOWLEDGMENT
This research was partially funded by the Industrial Technology Development Institute under the
Department of Science and Technology.
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Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas

  • 1. International Journal of Engineering Research and Development e-ISSN: 2278-067X, p-ISSN: 2278-800X, www.ijerd.com Volume 11, Issue 04 (April 2015), PP.60-66 60 Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas Aldrin D. Calderon1,2 , Blessie A. Basilia1,2 , Araceli M. Monsada1 , Edmar P. Casa1 , Lumen C. Milo1 , Marianito T. Margarito1 1 Industrial Technology Development Institute, Department of Science and Technology, DOST Compound, Bicutan, Taguig City, Philippines 2 School of Graduate Studies, Mapua Institute of Technology, Intramuros Manila, Philippines Abstract:- In this study, natural zeolites from the Philippines were modified using NaOH heat treatment and NaCl hydrothermal process. Pre-treatment using ferro-filtering and dealumination using different concentrations of HCl acid leaching were prepared prior to sodium activation. Heat treatment was performed using 5M NaOH at 80 °C for 72 hrs while 3 cycle hydrothermal process was performed using 5M NaCl at 10 psi for 1 hr. Diffraction pattern from XRD showed Heulandite (HEU) – Clinoptilolite (CLI) and Mordenite (MOR) framework for raw and acid pre-treated zeolites. There was a shift in HEU characteristic peak from 9.9084° and 8.91 Å to 9.6901° and 9.12 Å which can be attributed to the decrease of contribution of HEU type zeolite. The decrease in contribution enabled the peak to move towards 9.10 Å, value expected for MOR. However, it was found that presence of amorphous phase widens MOR structure on d-spacing 13.45 Å that created humps. Reduction of intensity peaks on HEU – CLI on 9.85°, 9.88° and 22.22° regions were observed attributed to acid leaching. The decline on this characteristic peaks implies severe degradation of crystal framework after heavy acid treatment although the framework was stable. Acid treated modified zeolites intensify Si/Al ratio due to dealumination. Sodium uptake along with higher Si/Al ratio was preferred for CO2 adsorption in a mixed gas system of CO2/CH4. Both NaOH heat treatment and NaCl hydrothermal process increase Na uptake as confirmed by EDS but the latter is preferred due to higher Si/Al ratio.. Keywords:- Dealumination, Na activation, Zeolite, Si/Al ratio, CO2 adsorption I. INTRODUCTION Natural and synthetic zeolites are long been used in various industrial applications [1-10]. Zeolite is a crystalline aluminosilicate with a three-dimensional framework structure that forms uniformly sized pores, channels and cavities of molecular dimensions [11]. Zeolite is made of negatively charged alumino-silicate building blocks that are stabilized by cations such as calcium and sodium [12-20]. Different classifications of zeolites exists, as a general rule, it is grouped in different frameworks based on the arrangement of T-atoms [21]. The structure of zeolites contains aluminum, silicon, and oxygen in regular frameworks with cations and water in the pores. Zeolites as the physical adsorbents for CO2 capture have been reviewed and explored by numerous researchers [22-26]. Since the gas adsorption reactions initially take place at the surfaces, the elements at the surface play an important role in the initial adsorption process [27-28]. Literatures on zeolite and its preparation with synthesis and modifications have been widely published to improve the adsorption characteristics of zeolites [29-34]. Hydrothermal treatment of zeolites involves the application of high pressure to effectively exchange native calcium cations into sodium [35-37]. This process is widely used to produce high quality modified zeolites. In this study, hydrothermal treatment was used and compared to reflux heat treatment and effects of acid pre-treatment. To date, limited published articles are seen on engineered Philippine natural zeolites. II. METHODOLOGY Natural local zeolites were acquired from Industrial Technology Development Institute under the Department of Science and Technology, Government of the Philippines, thru the Materials Science Division. These zeolites were prepared by continuous washing and passing thru a magnetic separator for ferro-filtering to remove ferrous substance then air-dried at 25 °C for 1 week. Effective separation of zeolite and fine iron particles from slurries passing by gravity flow is needed prior to modification since natural zeolites have high iron content embedded into their cavities which move into extra framework of zeolites upon high temperature calcination or steaming. Three (3) bags of 300 grams each were used for acid pre-treatment using hydrochloric acid with different molarity of 0M, 1M, 3M and 5M of HCl respectively that lasted for 48 hours at 25 °C. These
  • 2. Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas 61 acid pre-treated zeolites were washed using distilled water until pH is equal to 7. Upon washing, acid pre-treated zeolites were dried at 80 °C for 72 hours. Dried acid-treated zeolites were manually crushed and pounded until it passed thru Tyler mesh no. 100. Particle sizes were below 149 microns prior to sodium activation. There were three conditions considered in the sodium activation of zeolites. First condition was the heat-treatment process where acid pre-treated zeolites underwent NaOH reflux for 72 hours at 80 °C hot plate. Second condition was the hydrothermal condition where raw and acid pre-treated zeolites with 5M NaOH were subjected to a 3 cycle pressurized cooker of 10 psi for 1 hour. Third condition was 3 cycle hydrothermal modification using 1M and 5M NaCl for 1 hour in a pressure cooker of 10 psi. About 30 grams of 1M, 3M and 5M HCl acid pre-treated zeolites were subjected to 3M and 5M NaOH heat-treatment for 72 hours at 80 °C. Also, about 30 grams each of 3M and 5M HCl pre-treated zeolite were prepared for a 3 cycle 5M NaOH hydrothermal process where 10 psi for 1 hr process time is used each cycle. Washed until pH was equal to 7 and dried for 72 hrs at 80 °C, modified zeolites were pounded until particle sizes of less than 149 microns were acquired using Tyler mesh no. 100. Hydrothermal synthesis was performed after preparation of 1M and 5M NaCl in a beaker over 400 rpm magnetic stirrer for 2 hrs. About 20 grams of acid treated zeolites were mixed in autoclave bottles with 200 mL of 1M and 5M of NaCl separately in a pressure cooker of 10 psi for 1 hr. After 3 cycle hydrothermal modification, zeolite were washed until pH was equal to 7 and then dried for 72 hrs at 80 °C. III. RESULTS AND DISCUSSIONS Elemental spectra were acquired using Energy dispersive x-ray spectrometer (EDS) by Oxford Instruments attached to the Nano Helios Focused Ion Beam – Field Emission Scanning Electron Microscopy (FIB-FESEM) by FEI. Using less than 4 mm working distance and 20 – 25 kV beam voltage, spectra and mapping were captured to evaluate elemental composition of each acid pre-treated zeolite as presented in Fig. 1. EDS was used to acquire elemental composition of different types of zeolites. Using Helios FIB-FESEM coupled with EDS, elemental spectra were acquired and studied. Summary of elemental data for different treated zeolite from pre-treatment HCl acid pre-treatment, NaOH heat treatment, and NaCl hydrothermal process were presented in Fig. 2 and 3 showing elemental composition and Si/Al ratio respectively. Fig. 1 EDS complete elemental data mapping of acid pre-treatment for: (a) raw zeolite, (b) 1M HCl pre-treatment, (c) 3M HCl pre-treatment, (d) 5M HCl pre-treatment Using SHIMADZU X-Ray diffractometer LAB X, crystal structures of raw and treated zeolites were studied. Dried zeolite powdered samples about 3 μm thick were mounted in the XRD sample holder. The diffractometer model XRD-6000 using Cu K-alpha target was running at 40 kV and 30 mA. At a continuous scan mode and rate of 1 deg/min, scan range from 2 – 60° were evaluated using divergence slit of 1°, scattering slit of 1°, and receiving slit of 0.3 mm at 0.01° sampling pitch. Pre-treated zeolite using HCl were subjected to XRD for elemental analysis. Heulandite (HEU) – Clinoptilolite (CLI) and Mordenite (MOR) framework were (a) (b) (c) (d)
  • 3. Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas 62 detected based on diffractograms of ferro-filtered zeolite and different acid pre-treated zeolites as shown in different XRD patterns. After 1M and 5M NaCl hydrothermal synthesis was performed for 0M, 1M, 3M and 5M HCl pre- treated zeolites, samples were washed until pH was equal to 7 and then dried for 72 hours at 80 °C. Dried samples about 3 μm thick were mounted in the XRD sample holder where crystal structures were studied as well. 0 5 10 15 20 25 30 35 40 45 50 55 60 65 0 1000 2000 3000 4000 MOR 2.795 HEU HEU MOR MOR MOR 3.180 2.967 13.475 3.397 3.461 3.952 8.920 I(counts) 2THETA (deg) FERRO-FILTERED ZEOLITES 0 5 10 15 20 25 30 35 40 45 50 55 60 65 0 1000 2000 3000 4000 MOR FF + 1M HCl ACID TREATED HEU 3.960 I(counts) 2THETA (deg) MOR 13.556 HEU 8.954 MOR 3.468 3.397 MOR 3.178 2.8132.971 1.993 0 5 10 15 20 25 30 35 40 45 50 55 60 65 0 1000 2000 3000 4000 MOR 1.994 FF + 3M HCl ACID TREATED I(counts) 2THETA (deg) MOR 8.985 HEU 7.570 HEU 3.969 MOR 3.467 3.0002.818 0 5 10 15 20 25 30 35 40 45 50 55 60 65 0 1000 2000 3000 4000 MOR FF + 5M HCl ACID TREATED 1.998 2.827 MOR I(counts) 2THETA (deg) 9.120 HEU 3.988 HEU MOR 3.480 Fig. 2 Diffractogram of different concentration of acid pre-treatment for: (a) raw zeolite, (b) 1M HCl pre-treatment, (c) 3M HCl pre-treatment, (d) 5M HCl pre-treatment 0 5 10 15 20 25 30 35 40 45 50 55 60 0 1000 2000 3000 4000 5000 6000 SOD 2.095 SOD 2.554 SOD 2.798 SOD 3.612 I(counts) 2 THETA (deg) FF + 0M HCl + 5M NaOH FF + 1M HCl + 5M NaOH FF + 3M HCl + 5M NaOH FF + 5M HCl + 5M NaOH 5M NaOH HEAT TREATMENT PROCESS SOD 6.256 0 5 10 15 20 25 30 35 40 45 50 55 60 0 1000 2000 3000 4000 5000 6000 I(counts) 2 THETA (deg) FF + 5M HCl + 5M NaCl FF + 3M HCl + 5M NaCl FF + 1M HCl + 5M NaCl FF + 0M HCl + 5M NaCl FF + 5M HCl + 1M NaCl FF + 3M HCl + 1M NaCl FF + 0M HCl + 1M NaCl RAW 1M and 5M NaCl HYDROTHERMAL PROCESS Fig. 3 Diffractograms of modified zeolites (a) (b) (c) (d)
  • 4. Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas 63 Fig. 4 Cone bar graph of elemental composition of zeolites Fig. 5 Cone bar graph of Si/Al Ratio for different types of zeolite processing Diffraction pattern from XRD showed Heulandite (HEU) – Clinoptilolite (CLI) and Mordenite (MOR) framework for raw and acid pre-treated zeolites. Upon HCl acid pre-treatment, same structure were acquired. There was a shift in HEU characteristic peak from 9.9084° and 8.91 Å to 9.6901° and 9.12 Å which can be attributed to the decrease of contribution of HEU type zeolite. The decrease in contribution enabled the peak to move towards 9.10 Å, value expected for MOR. However, it was found that presence of amorphous phase widens MOR structure on d-spacing 13.45 Å that created humps. Also, reduction of intensity peaks on HEU – CLI on 9.85°, 9.88° and 22.22° regions were observed attributed to acid leaching. The decline on this characteristic peaks implies severe degradation of crystal framework after heavy acid treatment. Meanwhile, heat treatment using 5M NaOH showed different zeolite framework compared to raw and other modification. Comparison of interplanar spacing (d-spacing) and relative intensities similar to Kotashane et al. in 1986 proves an effective approach in defining zeolite frameworks. Characteristic peaks with diffraction pattern revealed sodalite octahydrate (SOD) type zeolite for 5M NaOH heat treatment modification, same structure formed by Baccouche et al. in 1998 for preparing sodalite octahydrate from 5M NaOH. A sodalite octahydrate framework was produced with literature value of window pore size 0.27 nm which is applicable for water separation. In general, zeolites with low Si/Al ratio (Si/Al < 5),
  • 5. Dealumination and Na activation of natural zeolite for CO2 adsorption on biogas 64 for example, zeolites A (LTA), X (FAU), and hydroxysodalite (SOD), are prepared from reaction mixtures with low Si/Al ratio and strong alkalinity. Sodalite has been theoretically suitable for hydrogen storage, water selective material and H2/CH4 separation because of low Si/Al ratio. Produced sodalite is an assembly of β- cages, the building blocks of many other zeolites which could be used for future study. The increase of alkalinity affects the induction and nucleation periods and speed up the crystallization of zeolites, forming new framework. The Si/Al ratio in the reaction system plays an important role in determining the structure and composition of the crystallized product. Alkaline solution contributes in dispersing the Si/Al ratio (T-atoms) during growth. Meanwhile, the effects of higher NaCl concentration on hydrothermal modification were seen in stacked pattern diffractogram of 1M and 5M NaCl. In 5M NaCl hydrothermal process, peak height significantly increases compared to 1M NaCl owing to higher intensity counts. Although strongest peaks did not alter much, reduction in characteristic HEU peaks was expected during hydrothermal process at 10 psi due to the severe pressure experienced by zeolite. With minimal shifts on MOR diffraction peaks for both acid pre-treatment and hydrothermal processes, MOR phase was far more resistant to chemical and thermal treatment than HEU type. The interferences of predominant peaks of other crystalline phase lead to minimal peak shifting but slight shrinking of zeolite cells. IV. CONCLUSIONS Sodium activation was successfully performed using heat treatment and hydrothermal treatment. Both NaCl hydrothermal process and NaOH heat treatment increase Na content of modified zeolites based on EDS spectra. Too much sodium and basic in nature, NaOH treated zeolites transformed into a new framework of sodalite type as confirmed by XRD peaks. Sodium as major cation present in modified zeolites performs the higher CO2 adsorption capacity compared to lower sodium but molecular sieving would be eliminated in the transport mechanism if sodalite type zeolite would be used for CO2/CH4 gas separation. In terms of sodium composition of zeolite and higher Si/Al ratio, NaCl hydrothermal process was preferred for CO2/CH4 gas separation experiment although sodium acquired during NaCl hydrothermal process was far less active than the NaOH heat treatment process. Moreover, dealuminated zeolite reduces the acidity of zeolite surface which is preferred since the zeolite must have basic surface in order for the CO2, as Lewis acid, to act on zeolite base sites. CO2 adsorption would be more effective in a basic surface of zeolite with higher Si/Al ratio for the adsorption of non-polar compounds such as CO2. ACKNOWLEDGMENT This research was partially funded by the Industrial Technology Development Institute under the Department of Science and Technology. REFERENCES [1]. Li C, Zhong H, Wang S, Xue J, Zhang Z. A novel conversion process for waste residue: Synthesis of zeolite from electrolytic manganese residue and its application to the removal of heavy metals. Colloids and Surfaces A: Physicochemical and Engineering Aspects. 2015; 470; 258-267. [2]. Cardoso AM, Horn MB, Ferret LS, Azevedo CMN, Pires M. Integrated synthesis of zeolites 4A and Na–P1 using coal fly ash for application in the formulation of detergents and swine wastewater treatment. Journal of Hazardous Materials. 2015; 287; 69-77. [3]. Duan A, Li T, Niu H, Yang X, Wang Z, Zhao Z, et al. Synthesis of a novel zeolite W and application in the catalyst for FCC gasoline hydro-upgrading. Catalysis Today. 2015; 245; 163-171. [4]. Iqbal N, Kadir MRA, Mahmood NHB, Yusoff MFM, Siddique JA, Salim N, et al. Microwave synthesis, characterization, bioactivity and in vitro biocompatibility of zeolite–hydroxyapatite (Zeo– HA) composite for bone tissue engineering applications. Ceramics International. 2014; 40; 16091- 16097. [5]. Zhu B, Myat DT, Shin J-W, Na Y-H, Moon I-S, Connor G, et al. Application of robust MFI-type zeolite membrane for desalination of saline wastewater. Journal of Membrane Science. 2015; 475; 167- 174. [6]. Insuwan W, Jungsuttiwong S, Rangsriwatananon K. Host–guest composite materials of dyes loaded zeolite LTL for antenna applications. Journal of Luminescence. 2015; 161; 31-36. [7]. Chong MN, Tneu ZY, Poh PE, Jin B, Aryal R. Synthesis, characterisation and application of TiO2– zeolite nanocomposites for the advanced treatment of industrial dye wastewater. Journal of the Taiwan Institute of Chemical Engineers. 2014; 0; 1-9. [8]. Kubička D, Kikhtyanin O. Opportunities for zeolites in biomass upgrading—Lessons from the refining and petrochemical industry. Catalysis Today. 2015; 243; 10-22.
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