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Clay materials modified with amino acids for purification processes of biogas and natural gas
Joanna Juźków
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Clay materials modified with amino acids for purification processes
of biogas and natural gas
Joanna Juźków
Instituto Superior Técnico, Lisbon, Portugal
Poznan University of Technology, Poznań, Poland
_________________________________________________________________________________________
ABSTRACT
Biogas and natural gas purification is an issue of a great industrial importance. Due to decrease of calorific
value of the fuel, corrosion and dry ince formation as a result of carbon dioxide presence in methane, the
concentration of CO2 needs to be reduced to ppm level. Adsorption on a natural sorbent has drawn the attention
of researchers recently, as a low-cost, environmentaly friendly and effective way of gas treatment. In the present
research samples of montmorillonite were intercalated with amino acids: glycine, arginine and L-histidine at pH
7 and pH 5 in order to enhance adsorption properties of the clay materials. The obtained adsorbents were
analyzed with FTIR, XRD, thermogravimetry with DSC and nitrogen adsorption-desorption. Conducted tests
confirmed retention of amino acid molecules in the clay structure and increase of porosity of materials in the
result of intercalation. Investigations of methane and carbon dioxide adsorption on the prepared samples were
conducted and adsorption isotherms were plotted. Clays intercalated with arginine and L-histidine adsorbed
more CO2 than in case of glycine. Materials prepared at pH 5 showed better results than samples obtained at pH
7. The adsorbent with the highest adsorption capacity was ARG-5 with 0.80 mmol/g of CO2 adsorbed. The most
selective material for CH4/CO2 separation was L-HIST-5, which up to 0.7 molar fraction of CH4 adsorbed only
CO2 from the mixture at relatively low pressure 100 kPa. The obtained results showed a promising possibility
for further application of intercalated clay materials in industrial gas treatment processes.
Keywords: adsorption, montmorillonite, amino acids, methane purification, carbon dioxide separation
_________________________________________________________________________________________
1. Introduction
Nowadays fossil fuels are by far the most dominant
energy sources and provide about 80% of total
world energy consumption. There is a strong
necessity to cut the utilization of fossil fuel energy
resources due to their significant environmental
impact connected with the emission of greenhouse
gases and pollutants [1]. As effect of fossil fuels
consumption, the atmospheric CO2 concentration
has been elevated from 280 ppm in pre-industrial
period to nearly 400 ppm in present times, what
contributed to a significant climate change [2]. One
of most promising renewable energy sources is
biomass, as it is considered as one of the most
suitable ways of energy storage, being a real
alternative to fossil fuels, as it is abundant, clean
and carbon neutral [3]. In Europe, biomass
currently accounts for around 2/3 of renewable
energy and will play a key role in reaching the
Clay materials modified with amino acids for purification processes of biogas and natural gas
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target approved by the renewable sources by 2020
[1]. Biogas is produced by anaerobic digestion of
biomass, in the industry is generated at sewage
treatment plants, landfills, sites with industrial
processing industry and at digestion plants for
agricultural organic waste [4]. Biogas is an
alternative for energy production, that has
advantages of being eco-friendly source of energy,
in that the calorific value of biogas is equal to that
of half litre of diesel oil. (6 kWh/m3) [5]. The final
result of a series of decomposition reactions of
organic matter are methane, carbon dioxide and
water as main products [6]. When CO2 and other
impurities are removed during the upgrading
process, the methane concentration increases and
thus the resulting biomethane can be utilized as an
alternative to natural gas [7]. Natural gas itself,
although cannot be referred to as the green energy,
its use has many advantages over the use of other
conventional fuels. Burning NG produces less CO2
and more water vapour per energy unit than burning
gasoline or diesel [8]. For methane distribution
through pipelines or liquefaction in order to
transport it for long distances the impurities
contained in methane (in form of biogas or natural
gas) need to be removed [9]. Presence of CO2
lowers calorific value of the fuel and can cause dry
ice formation. Methane for domestic use is required
to have 97% or higher purity [10]. Among different
technologies developed for methane treatment,
adsorption on the low-cost adsorbents in gaining
more attention, as method relatively cheap, simple
and environmental-friendly. Natural clays are an
interesting group of adsorbents, regarding their
layered structure and extraordinary properties, like
ion-exchange, swelling and possibility of
intercalation of particles between the layers [11-13].
Due to them it is possible to introduce molecules of
other compounds into the clay’s structure, tuning
their properties.
In the present work a natural clay - montmorillonite
(MMT) was intercalated with three different amino
acids: glycine, arginine and L-histidine in order to
enhance its adsorptive properties. Amino acid
intercalated clay materials are capable of CO2
retention due to the presence of amine groups in the
amino acid structure. Glycine, as the simplest
amino acid, contains only one NH2 group in the
structure. L-histidine and arginine, having
additional basic amino groups side chains are
expected to show enhanced adsorption properties
[13, 14]. Amino acids can be considered as green
compounds, as being one of main building blocks
of living organisms are eco-friendly and do not
cause contamination when released to the
environment.
2. Materials preparation
Natural montmorillonite (MMT) clay from
Wyoming, USA has been used as a raw material for
adsorbents preparation. For the clay’s surface
functionalization three different amino acids:
glycine, arginine and l-histidine (Sigma Aldrich,
purity >99%) were used. Two samples, at pH 5 and
pH 7 were prepared for each kind of amino acid and
also a sample of non-intercalated MMT. In order to
prepare amino acid intercalated clay adsorbents the
following procedure was applied. 2 g of clay was
added to 100 mL of distilled water and mixed for 3
h using magnetic stirrer. 50 mL of 0.03 M solution
of amino acid was prepared by dissolving adequate
amount of amino acid in distilled water. All
solutions were obtained at room temperature. Then,
the amino acid solution was added to the clay and
pH of the mixture was adjusted to the required
value using 0.05 M HCl solution. The acid solution
was prepared by dilution of HCl solution (Carlo
Erba, 37%) with distilled water. The clay mixture
was mixed with amino acid solution overnight in
Clay materials modified with amino acids for purification processes of biogas and natural gas
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the room temperature. The next day it was removed
from stirrer and centrifuged with centrifuge (NF400
– N400R Nüve). Next the supernatant was
discarded and the sample was washed with distilled
water at room temperature and dried in the oven
overnight. The obtain material was milled with a
mortar and stored in a plastic container. Six kinds
of adsorbents were prepared: three at pH 7,
intercalated with glycine (GLY-7), arginine (ARG-
7) and L-histidine (L-HIST-7). Also three materials
at pH 5 were obtained, GLY-5, ARG-5 and L-
HIST-5, respectively. Schema of adsorbents
preparation is shown in the Fig. 1.
Fig. 1. Schema of adsorbents preparation.
3. Characterization methods
FTIR spectra of prepared adsorbents were collected
along with spectra of pure amino acids used for
montmorillonite intercalation – glycine, arginine
and L-histidine. The analysis was conducted using
KBr pellet method. First KBr pellet was obtained
by milling KBr with a mortar and pressurizing it.
The KBr pellet was used to obtain the background
spectra. The pellets of investigated samples were
prepared by mixing adsorbent material with KBr in
proportion 2:3, milling with a mortar and
pressurizing to produce the final pellet. The sample
spectra was collected by subtraction of background
KBr spectrum from the spectrum of pellet
containing KBr and sample material. The
investigation of FTIR was conducted with use of a
Nicolet 6700 Fourier transform IR
spectrophotometer (256 scans, resolution 4 cm-1
) in
the wavenumber range from 400 to 4000 cm-1
.
X-ray diffraction spectra of pressed powder
samples were prepared for pure MMT and each
type of amino acid-intercalated MMT. X-ray
powder diffraction patterns in range from 3o to 10
o
were obtained with a Phillips PW 1730
diffractometer with automatic data acquisition
(APD Phillips v3.6B software using a Cu anode
(λ=1.5406 Ǻ)).
The values of interatomic spacing were calculated
on the basis of θ values from the Bragg law:
, where: d – the interplanar distance
[Ǻ], θ – the scattering angle [o], n – the positive
integer (n=1), λ – the wavelength of incident wave
(λ=1.5406 Ǻ). The clay expansion in result of
intercalation was calculated by subtracting the
value of the interlayer spacing of MMT from the
value of interlayer spacing of intercalated materials.
Experiments of thermogravimetry with differential-
scanning calorimetry were conducted using an
apparatus Setaram TG-DSC 111. All the samples
were analyzed regarding mass loss and heat flow
during heating. The analysis was conducted in the
temperature range from 25 oC to 700
oC and speed
5 oC/min.
In the nitrogen adsorption-desorption analysis the
capillary condensation of nitrogen inside pores
allows for evaluation of porous volume and pore
size distribution in the sample. Clay adsorbents
were analyzed by nitrogen (Air Liquide, 99.999%)
adsorption-desorption with NOVA 2200e
Quantachrome at -196 oC. The samples were
previously degassed for 2.5 h at 150 oC under
vacuum conditions.
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4. CO2 and CH4 adsorption measurements
Pure gas adsorption isotherm experiments were
performed on a high-pressure adsorption line. The
central element of the adsorption line was a
stabilization cell of calibrated volume enclosed
between three valves and connected with pressure
tranducer, which allowed for precise measurement
of pressure of the gas inside. The left valve was
connected to the pressurized gas bottles (switched
between methane, carbon dioxide and helium), that
supplied the gas used for adsorption properties
investigation. The right valve was connected to the
diffusion pump and allowed for creating vacuum
conditions inside the line and degassing of the
sample. The bottom valve was connected to the cell
with powder of investigated adsorbent material
inside. The cell and the stabilization cell were
submerged in the water bath, in order to conduct the
experiments in the conditions of controlled
temperature. For degassing of the sample vacuum
pump and diffusion pump were applied in the line.
The liquid nitrogen was used for removal of
contaminations from the line by their condensation
in the trap. The general scheme of high pressure
adsorption line installation is presented in the Fig 2.
Fig. 2. Scheme of the adsorption line
The sample powder ca. 1.5 g was placed inside the
cell, which was connected to the adsorption line
and degassed under vacuum conditions with
diffusion pump for 2.5 h at 150 oC using oven with
thermocouple for temperature control. Next, the cell
was cooled down to the room temperature and the
cell factor measurements were conducted. In order
to calculate the cell factor extrapure helium
(Praxair, purity 99.999%) was introduced into the
cell at pressures increasing accordingly to the order:
200, 400, 600 and 1000 kPa. After opening the cell
valve, the resulting pressure decrease was used to
calculate the cell factor. For adsorbents prepared at
pH 7 the cell factor was calculated at 25oC, for
adsorbents at pH 5 at 25 and 45 oC. The cell with
sample and calibrated cell were submerged in
waterbath for temperature control. After finishing
the calibration helium was eliminated from the cell
under vacuum.
Next, investigation of adsorption isotherms were
conducted using pressurized gases: methane (Air
Liquide, purity 100%) and carbon dioxide (Criolab,
purity 99.995%). In order to obtain the isotherms
portions of gas were purged into the cell starting
from 200 kPa and doubling the pressure each time
up to the value of 1000 kPa. The value of pressure
drop was noted after reaching equilibrium pressure
and the amount of the gas adsorbed was calculated.
After finishing the experiment the powder was
cleaned removing the gas by heating for ca. 1 h at
150 oC in vacuum conditions.
On the basis of obtained results adsorption
isotherms of carbon dioxide and methane
adsorption on amino acid intercalated MMT were
plotted. The isotherms show results obtained at 25
oC for clay based adsorbents at pH 7 and at 25 and
45 oC for adsorbents produced at pH 5. The
obtained results were fitted into virial equation. The
analytical expressions were further applied for
calculations of selectivity of materials and
adsorption of carbon dioxide and methane from the
binary mixture.
Clay materials modified with amino acids for purification processes of biogas and natural gas
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Table 1. θ values for basal peak obtained in XRD plots for MMT and amino acid modified MMT materials, corresponding
interlayer spacing and expansion of MMT in the effect of amino acid intercalation.
MMT pH 7 pH 5
GLY-7 ARG-7 L-HIST-7 GLY-5 ARG-5 L-HIST-5
θ [o] 3.600 3.4845 3.3230 3.4045 3.4300 3.4215 3.4170
d [Ǻ] 12.27 12.67 13.29 12.97 12.86 12.91 12.92
expansion [Ǻ] - 0.40 1.02 0.70 0.59 0.64 0.65
Fig. 3. XRD plots for amino acid modified materials obtained at pH 7 and pH 5.
5. Results and discussion
Regarding the data obtained with FTIR method for
amino acid intercalated samples, the FTIR analysis
could not provide reliable proof for the presence of
amino acid molecules in the clay structure for all
the investigated materials. According to a big
dilution of amino acids in clay material in was very
difficult to obtain noticeable peaks for respective
peaks in the spectra. Also the peaks coming from
the raw material – montmorillonite influenced to
the great extent the plot of spectra, covering the
presence of amino acids. Materials obtained at pH 7
gave no characteristic peaks visible in spectra and
only peaks characteristic for MMT were observed.
Samples prepared at pH 5 showed some peaks that
could correspond to the amino acids presence,
although it was hard to relate them to specific
vibrations.
In XRD analysis a characteristic, strong and sharp
basal reflection for the MMT plot can be observed
for θ equal to 3.6o. For all the amino acid modified
samples shift of the basal peak to smaller θ values
was noticed (Fig. 3.). It indicates increase of
interlayer spacing in the structure of investigated
materials, what can be explained by expansion of
clay structure caused by intercalation of amino acid
molecules. The results of calculated interlayer
spacing along with values of MMT structure
expansion are presented in the Table 1.
The basal spacing for the pure MMT was calculated
as 12.27 Ǻ, which is characteristic value of basal
spacing for clay materials, usually enclosed
between 12 to 14 Ǻ. It can be noticed that the
greatest expansion of spacing is present in case of
ARG-7, equal to 1.02 Ǻ, which is followed by L-
HIST-7 with the value of 0.70 Ǻ. The least
expanded material of all the investigated samples
was GLY-7 with expansion corresponding to 0.40
Ǻ. Adsorbent samples obtained at pH 5 presented
medium expansion with values located between
marginal results for materials at pH 7. Among
0
20
40
60
80
100
3 4 5 6 7 8 9 10
inte
nsi
ty [
a. u
.]
2θ [o]
pH 5
MMTGLYARGL-HIST
0
20
40
60
80
100
3 4 5 6 7 8 9 10
inte
nsi
ty [
a. u
.]
2θ [o]
pH7
MMTGLYARGL-HIST
Clay materials modified with amino acids for purification processes of biogas and natural gas
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Fig. 4. TG DSC plots for adsorbents prepared at pH 7 and pH 5.
them the most expanded material was L-HIST-5
amounting to 0.65 Ǻ. The least expanded material
was GLY-5 with expansion of 0.59 Ǻ. In the TG
DSC analysis (Fig. 4) the raw MMT the first loss of
mass of ca. 7% was observed between 30 and 115
oC, which contributed to the release of water
physically adsorbed on the clay. It corresponded to
the endothermic peak that could be observed on the
heat flow in the same range of temperatures. During
further heating the mass of MMT remained
constant until 600 oC. The sharper decrease of mass
beyond 600 oC resulted from destruction of clay
structure under high temperature. For intercalated
clays prepared at pH 7 analogous mass loss due to
water evaporation can be noticed, but with smaller
mass decrease indicated; approximately 4% for L-
HIST-7 and 6% for GLY-7 and ARG-7. Next,
another small decrease of mass (around 1%) was
observed, which also reflected in slight
endothermic peak on the heat flow plot, that
contributed to the loss of water adsorbed in the
pores. Further slow decrease of mass was observed
for GLY-7 and L-HIST-7 (ca. 5% and 6%
respectively) in the region of 300 to 600 oC In case
of ARG-7 no significant mass decrease was
observed in this region. However, corresponding
strong endothermic decrease in the heat flow can be
noticed. It indicated decomposition of adsorbed
amino acids from the interlayer space of clays. In
case of materials obtained at pH 5 analogical mass
loss along with characteristic endothermic peaks
can be observed in the range of 15 to 115 oC
contributing to the water loss. The mass loss
contributing to amino acids removal amounted to
13% for ARG-5, 6% for GLY-5 and 7% for L-
HIST-5., what indicates more efficient intercalation
Table 2. Porosity and surface properties characteristics of pure MMT and amino acids modified MMT materials.
-18
-13
-8
-3
2
70
75
80
85
90
95
100
15 215 415 615
he
at fl
ow
[mV
]
mas
s [%
]
temperature [oC]
pH7MMT GLY ARG L-HIST
-18
-13
-8
-3
2
70
75
80
85
90
95
100
15 215 415 615
he
at fl
ow
[mV
]
mas
s [%
]
temperature [oC]
pH5MMT GLY ARG L-HIST
MMT pH 7 pH 5
GLY-7 ARG-7 L-HIST-7 GLY-5 ARG-5 L-HIST-5
BET surface area [m2/g] 20 34 22 14 35 35 9
micropore volume [cm3/g] 0 0 0 0 0 0 0
micropore area [cm2/g] 1 0 0 0 0 0 2
external surface area [cm2/g] 18 34 22 14 35 35 7
total pore volume [cm3/g] 0.032 0.054 0.044 0.037 0.072 0.074 0.025
Clay materials modified with amino acids for purification processes of biogas and natural gas
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The results of nitrogen adsoption-desorption
analysis were gathered in the Table 2. GLY-5 and
ARG-5 show the best porosity and surface
properties among all the adsorbents prepared, with
surface area amounting to 35 m2/g and total pore
volume 0.074 cm3/g for ARG-5 and 0.072 cm
3/g for
GLY-5. Both adsorbents intercalated with L-
histidine; L-HIST-7 and L-HIST-5 exhibited
relatively low development of surface area, 14
cm2/g and 7 cm
2/g respectively, which was lower
than for MMT with 18 cm2/g. ARG-7 and GLY-7
presented medium values of surface area with 22
cm2/g and 34 cm
2/g respectively and pore volume
0.044 cm3/g and 0.054 cm
3/g respectively.
As presented in the Fig. 5, at pH 7 the highest
adsorption capacity towards carbon dioxide was
shown by ARG-7 with the value of 0.46 mmol/g at
high pressures and it was the only material among
intercalated clays, that showed better adsorption
abilities than raw MMT with CO2 retention
amounting to 0.25 mmol/g at high pressures. Both
GLY-7 and L-HIST-7 exhibited lower amount of
CO2 adsorbed with results of 0.08 and 0.023
mmol/g respectively. In case of methane
adsorption, amounts of gas adsorbed were lower
than for carbon dioxide for all the investigated
adsorbents. Amount of CH4 retained by GLY-7 was
very low (0.003 mmol/g) and below the sensitivity
of the method. For this reason results of this
adsorption isotherm are not presented on the graph.
Fig. 5. Adsorption isotherms of carbon dioxide and methane adsorption at 25oC on amino acid intercalated MMT samples
prepared at pH 7.
Fig. 6. Adsorption isotherms of carbon dioxide and methane adsorption at 25oC on amino acid intercalated MMT samples
prepared at pH 5.
0
0,2
0,4
0,6
0,8
1
0 200 400 600 800 1000
nad
s[m
mo
l/g]
p [kPa]
CO2
ARG-7 L-HIST-7 GLY-7 MMT
0
0,2
0,4
0,6
0,8
1
0 200 400 600 800 1000
nad
s[m
mo
l/g]
p [kPa]
CH4
L-HIST-7 ARG-7
0
0,2
0,4
0,6
0,8
1
0 200 400 600 800 1000
nad
s[m
mo
l/g]
p [kPa]
CO2
ARG-5 L-HIST-5 GLY-5 MMT
0
0,2
0,4
0,6
0,8
1
0 200 400 600 800 1000
nab
s[m
mo
l/g]
p [kPa]
CH4
GLY-5 ARG-5 L-HIST-5
Clay materials modified with amino acids for purification processes of biogas and natural gas
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Fig. 7. Adsorption isotherms of carbon dioxide adsorption at 25oC and 45oC on amino acid intercalated MMT samples
prepared at pH 5.
Methane retained on ARG-7 and L-HIST-7 reached
value of 0.11 mmol/g. Due to low amounts of gases
adsorbed at 25 oC, for the materials prepared at pH
7 adsorption at higher temperature (45 oC) was not
conducted.
For pH 5 (Fig. 6.) the amounts of carbon dioxide
adsorbed increased for all the intercalated clays in
comparison to the values obtained at pH 7, with the
best result for ARG-5, equal to 0.80 mmol/g. It was
the highest amount of carbon dioxide adsorbed
among all experiments conducted in presented
research. The second value belonged to L-HIST-5
with 0.53 mmol/g of CO2 adsorbed. The material of
lowest adsorptive properties was GLY-5, which
retained 0.32 mmol/g. All adsorbents prepared at
pH 5 exhibited better adsorption of carbon dioxide
than raw MMT material. ARG-5 and L-HIST-5 are
capable of adsorbing over 0.4 mmol/g of CO2 at
pressures lower than 200 kPa. It indicates the
possibility to conduct the adsorption process at
lower pressure, what is favourable from technical
and economical point of view for further
implementation to industrial-scale processes. The
amounts of methane adsorbed were significantly
lower than CO2.
As it can be noticed in Fig. 7, at 45 oC ARG-5
showed the highest adsorption properties with 0.72
mmol/g of all the samples investigated at pH 5.
Although L-HIST-5 presented slightly lower results
with final amount of carbon dioxide adsorbed equal
to 0.64 mmol/g, it obtained better results than
ARG-5 at lower pressures, reaching 0.5 mmol/g at
240 kPa. GLY-5 was the material with the lowest
adsorptive properties, reached 0.32 mmol/g. It
should be pointed out, that even though it was
expected, that at higher temperature the adsorbents
would exhibit lower properties of adsorption, GLY-
5 and L-HIST-5 reached higher amounts of carbon
dioxide adsorbed at 45 oC than in case of the
experiment conducted at 25 oC.
Fig. 8. Selectivity of aminoacid intercalated MMT
adsorbents against pressure.
0
0,2
0,4
0,6
0,8
1
0 200 400 600 800 1000
nad
s[m
mo
l/g]
p [kPa]
25 oCL-HIST-5 ARG-5 GLY-5 MMT
0
0,2
0,4
0,6
0,8
1
0 200 400 600 800 1000
nad
s [m
mo
l/g]
p [kPa]
45 oCL-HIST-5 ARG-5 GLY-5
1
21
41
61
81
101
121
141
161
181
201
0 200 400 600 800 1000
Se
lectivity
p / kPa
L-HIST-5
ARG-5
GLY-5
L-HIST-7
ARG-7
Clay materials modified with amino acids for purification processes of biogas and natural gas
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Fig. 9. Phase diagrams at 100 kPa describing separation of CH4 between gaseous and adsorbed phase as a function of mole
fraction of CH4 in adsorbed phase (left up) and phase diagrams for L-HIST-7, ARG-7, L-HIST-5, ARG-5 and GLY-5.
Among materials used for experiences L-HIST-5
presented the best selectivity properties. (Fig. 8.)
The second adsorbent was ARG-7 followed by
ARG-5. The least selective materials were L-HIST-
7 and GLY-5. It is remarkable, that for while
samples with low selectivity, the selectivity is not
much dependent on pressure (GLY-5, L-HIST-7,
ARG-5). For materials highly selective, selectivity
grows significantly with increase of pressure.
The graphs presented in the Fig 9. show that L-
HIST-5 has best adsorptive properties among all the
investigated samples. Up to 0.7 molar fraction of
CH4 contained in the mixture, no adsorption of this
gas is exhibited and only CO2 is being retained with
amount of 0.3 mmol/g of CO2 adsorbed. The
retention of CO2 remains predominant up to 0.96
molar fraction of CH4 in the binary mixture. ARG-7
shows exclusivity of CO2 adsorption until 0.25
molar fraction of CH4 with retention of CO2 equal
to 0.34 mmol/g at this point. Interesting properties
were also shown by ARG-5 with the highest
retention of both pure gases, with values amounting
to 0.44 mmol/g for CO2 and 0.1 mmol/g for CH4.
Very poor selectivity and adsorption properties
were shown by L-HIST-7 and GLY-5.
6. Conclusions
Intercalation process was successful for all the
materials prepared. Due to insertion of amino acid
molecules into the interlayer space expansion of
montmorillonite structure was observed on XRD
spectra, as well as for all the samples, except for L-
HIST-5, increase of surface area and total pore
volume was noted. The CO2 adsorption was
strongly enhanced by intercalation with amino
acids.Higher adsorption capacity was obtained for
adsorbents prepared at pH 5. It can be explained by
greater retention of amino acids by clay material at
this pH due to protonation of amine groups of
amino acids, what causes the increase of their
availability for carbon dioxide adsorption. The
material with highest adsorption capacity towards
CO2 was ARG-5 with 0.80 mmol/g. Both arginine
0
0,1
0,2
0,3
0,4
0,5
0 0,5 1
ad
so
rbed
am
ount / m
mo
l g -
1
yCH4
CO2CH4Total
ARG-7
0
0,1
0,2
0,3
0,4
0,5
0 0,5 1
ad
so
rbed
am
ount / m
mo
l g -1
yCH4
CO2
CH4
Total
L-HIST-7
0
0,1
0,2
0,3
0,4
0,5
0 0,5 1
ad
so
rbed
am
ount / m
mo
l g -
1
yCH4
CO2CH4Total
GLY-5
0
0,1
0,2
0,3
0,4
0,5
0 0,5 1
ad
so
rbed
am
ount / m
mo
l g -
1
yCH4
CO2CH4Total
ARG-5
0
0,1
0,2
0,3
0,4
0,5
0 0,5 1
ad
so
rbed
am
ount / m
mo
l g -
1
yCH4
CO2
CH4
Total
L-HIST-5
0
0,2
0,4
0,6
0,8
1
0 0,5 1
y CH
4
xCH4
L-HIST-5
ARG-5
GLY-5
L-HIST-7
ARG-7
Clay materials modified with amino acids for purification processes of biogas and natural gas
Joanna Juźków
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and L-histidine intercalated clays showed
satisfactory results and their adsorption capacity
towards carbon dioxide was higher than in case of
raw montmorillonite. Adsorption on glycine
intercalated samples did not give promising results.
For the tests conducted at temperature 45 oC at pH
5, the amount of carbon dioxide adsorbed was
higher for ARG-5 and GLY-5 than at 25 oC.
Retention of methane by intercalated clays gave
lower results than for CO2 for all materials. In terms
of selectivity L-HIST-5 was the best adsorbent,
adsorbing exclusively CO2 up to 0.7 molar fraction
of CH4 in the binary mixture and predominant CO2
retention up to 0.96 molar fraction of CH4. Amino
acid modified montmorillonite adsorbents showed
promising results for CO2 and CH4 separation.
Regarding their low-cost, environmental friendly
character and selectivity, they can be successfully
applied in the industrial separation processes.
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