Subscriber access provided by University of Florida | Smathers Libraries 2
2
Clathrate-based CO Capture from CO-rich Natural Gas and Biogas Jiyeon Lim, Wonjung Choi, Junghoon Mok, and Yongwon Seo ACS Sustainable Chem. Eng., Just Accepted Manuscript • DOI: 10.1021/ acssuschemeng.8b00712 • Publication Date (Web): 14 Mar 2018 Downloaded from http://pubs.acs.org on March 15, 2018
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
1
Clathrate-based CO2 Capture from CO2-rich Natural
2
Gas and Biogas Jiyeon Lim†, Wonjung Choi†, Junghoon Mok†, and Yongwon Seo†*
3 †
4 5
School of Urban and Environmental Engineering, Ulsan National Institute of Science and Technology, 50 UNIST-gil, Ulju-gun, Ulsan 44919, Republic of Korea
6
*
Corresponding author. Tel: +82-52-217-2821. Fax: +82-52-217-2859 E-mail address:
[email protected] (Y. Seo)
ACS Paragon Plus Environment
1
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 2 of 38
7
ABSTRACT. In this study, clathrate-based CO2 capture was investigated in the presence of
8
thermodynamic promoters such as tetrahydrofuran (THF) and tetra-n-butyl ammonium chloride (TBAC)
9
for upgrading CO2-rich natural gas and biogas. The phase equilibria, gas uptakes, gas
10
composition measurements, and spectroscopic analyses of CH4 (50%) + CO2 (50%) + promoter
11
clathrates were examined with a primary focus on the effects of thermodynamic promoters on
12
clathrate stability and cage filling behavior. The addition of THF and TBAC significantly enhanced
13
the thermodynamic stability of CH4 (50%) + CO2 (50%) clathrates.
14
spectroscopy clearly revealed that CO2 and CH4 are enclathrated in the clathrate cages. THF
15
solutions demonstrated a faster growth rate of clathrates but CO2 was less selective than CH4 in
16
the THF clathrate phase due to the lower thermodynamic stability of the CO2 + THF clathrate
17
compared to the CH4 + THF clathrate. TBAC solutions produced higher CO2 selectivity in the
18
semi-clathrate phase due to the presence of distorted small cages which have a strong preference
19
for CO2 molecules. The experimental results demonstrated that CO2 selectivity in the clathrate
20
phase can be influenced by thermodynamic stability, cage shape and dimension, and cage filling
21
behavior in the presence of thermodynamic promoters and thus, a suitable promoter and their
22
optimum concentration should be carefully determined in designing and operating clathrate-
23
based CO2 capture from natural gas or biogas.
13
C NMR and Raman
24 25
Keywords: Clathrate hydrate, CO2 capture, Gas upgrading, Promoters, Biogas
ACS Paragon Plus Environment
2
Page 3 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
26
Introduction
27
Methane (CH4) is a main component of natural gas, and it has recently been found in unconventional
28
forms, such as shale gas and natural gas hydrates. CH4 is also generated from biogas or landfill gas by the
29
anaerobic decomposition of organic substrates1. The importance of natural gas as an energy source has
30
been increasing because it has higher energy efficiency and less of an effect on global warming than coal
31
and oil2. However, natural gas and biogas contain some impurities, including carbon dioxide (CO2) and
32
hydrogen sulfide (H2S), which are called sour gases and can reduce the calorific value of natural gas and
33
biogas3. A significant number of natural gas fields remain untapped due to the high concentration of sour
34
gas, and some natural gas fields contain even more than 50% CO2 4. Also, biogas typically consists of 50–
35
75% CH4 and 25–50% CO2 5. To increase the energy content of the gas, the upgrading of natural gas and
36
biogas should be performed by separating CO2 from the gas mixture and, thereby, concentrating CH4.
37
Conventional CO2 separation or capture methods include chemical absorption, physical adsorption,
38
cryogenic distillation, and membrane separation6. Amine-based chemical absorption is one of the
39
conventional and representative methods for CO2 capture from flue gas, but it is applicable only for feed
40
gas with lower CO2 concentrations, and it has also solvent degradation and corrosion problems. Other
41
methods have their own drawbacks, such as low capture efficiency, intensive energy usage, and low
42
reusability of separation media. Recently, clathrate-based gas separation has been suggested as a
43
promising option for capturing greenhouse gases with higher concentrations7–16.
44
Clathrate hydrates are non-stoichiometric crystalline compounds which incorporate gas molecules (guest)
45
into hydrogen-bonded water cages (host) under high pressure and low temperature conditions, and they
46
can be generally classified into true clathrates and semi-clathrates17. Gas hydrates which belong to true
47
clathrates exist in three different structures: structure I (sI), structure II (sII), and structure H (sH)17, 18. Each
ACS Paragon Plus Environment
3
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 4 of 38
48
structure consists of differently sized and shaped cages. Semiclathrates share many physical and chemical
49
features with true clathrates, but the primary difference is that in true clathrates guest molecules are not
50
physically bonded to host water cages whereas in semiclathrates some guest molecules can participate in
51
forming clathrate cage structures. Quaternary ammonium salts (QASs) are known as semi-clathrate
52
formers and their cations can be incorporated into large cages whereas their anions can take part in
53
building up cage structures by replacing some host water molecules19-22.
54
CO2 can be captured by formation of the clathrate hydrate and CO2 capture from CO2-rich natural gas and
55
biogas using clathrate formation is affected by the equilibrium pressure difference between CH4 clathrate
56
and CO2 clathrate. However, there are main drawbacks of clathrate-based CO2 capture; it requires high
57
pressure and low temperature for clathrate formation and similar molecular sizes of CH4 and CO2
58
could result in the lower separation efficiency. Natural gas extracted from the reservoir with high
59
pressure does not need additional pressurization for clathrate formation23, but biogas is produced at
60
atmospheric pressure. Therefore, chemical additives, called thermodynamic promoters, are used to
61
enhance the thermodynamic stability of clathrates, and they can reduce the equilibrium pressure at any
62
given temperature or raise the equilibrium temperature at any given pressure24. Also, the extent of
63
improved thermodynamic stability of gas hydrates in the presence of thermodynamic promoters varies
64
depending on guest gases and thus, thermodynamic promoters can exert an influence on gas separation
65
efficiency. Thermodynamic promoters that have been commonly used are cyclic ethers and QAS
66
materials. Tetrahydrofuran (THF), one of the cyclic ethers, is a water-soluble sII clathrate former which
67
can function as both a thermodynamic and a kinetic promoter25, 26, and it can facilitate gas hydrate
68
formation at milder conditions 27. Tetra-n-butylammonium chloride (TBAC) is a semi-clathrate
69
former which has a large storage capacity and high thermodynamic stability among various
70
QASs19. TBAC can form semi-clathrates under atmospheric pressure and the semi-clathrate
ACS Paragon Plus Environment
4
Page 5 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
71
possess vacant small cages that can be used for capturing small-sized gas molecules, so they can
72
be effectively applied for gas separation and storage28-35.
73
Even though various works on the phase equilibria and formation kinetics of CH4 + CO2
74
clathrates have been reported in the literatures16,25,36, the effect of thermodynamic promoters on
75
cage filling behavior of guest molecules in different clathrate structures has not yet been clearly
76
examined for clathrate-based CO2 capture from natural gas and biogas. In this study, the gas
77
mixture of CH4 (50%) + CO2 (50%) was used as a target gas simulating CO2-rich natural gas and
78
biogas, and THF and TBAC were selected as thermodynamic promoters for clathrate formation.
79
The precise and unique patterns of CH4 (50%) + CO2 (50%) + promoter (THF and TBAC)
80
clathrates were investigated with a primary focus on the effects of thermodynamic promoters on
81
clathrate stability and cage filling behavior. The thermodynamic stability of CH4 (50%) + CO2
82
(50%) + promoter (THF and TBAC) clathrates were experimentally measured at two different
83
promoter concentrations (1.0 mol% and stoichiometric concentrations of each clathrate
84
structure). The enclathration of guest molecules in the clathrate cages of different structures were
85
observed using
86
clathrates were examined by measuring the amount of gas consumption during clathrate
87
formation. CO2 concentration changes in the vapor phase during clathrate formation and CO2
88
concentrations in the vapor and clathrate phases after completion of clathrate formation were
89
measured using gas chromatography to examine CO2 selectivity, depending on the types and
90
concentrations of thermodynamic promoters.
13
C NMR and Raman spectroscopy. The gas uptakes and growth rates of the
ACS Paragon Plus Environment
5
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 6 of 38
91
Experimental Section
92
Materials and Methods
93
CH4 gas (99.95%), CO2 gas (99.99%), and a gas mixture of CH4 (50%) + CO2 (50%) were
94
supplied by MS Gas, Ltd. (Republic of Korea). Tetrahydrofuran (THF, 99%) and tetra-n-butyl
95
ammonium chloride (TBAC, 97%) were purchased from Sigma-Aldrich Chemical Co. (USA).
96
Double distilled, deionized water was used in this study. The experimental apparatus was
97
specially designed in order to measure the accurate phase equilibrium by tracking temperature
98
and pressure during clathrate formation and dissociation. A high-pressure equilibrium cell with
99
an internal volume of 250 cm3 was made of 316 stainless steel, and the inner content of the cell
100
was vigorously mixed with an impeller-type agitator (350 rpm). The cell was immersed in a
101
water bath, and the temperature of the water bath was controlled by an external circulator (RW-
102
2025G; JEIO Tech, Republic of Korea). The temperature was measured using a thermocouple
103
which was calibrated with an ASTM 63C liquid-in-glass thermometer (H-B Instrument
104
Company, USA) with an accuracy of ± 0.1 K. The pressure was measured using a pressure
105
transducer (Model S-10; Wika, Germany) which was calibrated by a Heise Bourdon tube
106
pressure gauge (CMM-137219; Ashcroft Inc., USA) within the experimental range. The
107
uncertainties associated with the temperature and pressure measurement are 0.1 K and 0.02 MPa,
108
respectively.
109
Phase equilibrium measurement
110
The high-pressure equilibrium cell was initially filled with 70 cm3 of the solution with
111
thermodynamic promoters (TBAC and THF). After assembling the apparatus, ventilation was
112
conducted several times to remove residual air from the cell. Then, the gas mixture (CO2 + CH4)
ACS Paragon Plus Environment
6
Page 7 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
113
was injected into the cell until the desired experimental pressure was obtained. A stepwise
114
heating and cooling method was applied under an isochoric condition in order to accurately
115
measure clathrate phase equilibria. The cell was slowly cooled from 298 K until the pressure in
116
the cell abruptly dropped due to the clathrate formation. After sufficient time was given for
117
complete clathrate formation, the temperature was increased in steps of 0.1 K/90 min to
118
dissociate the clathrates. As the clathrates dissociated, the pressure in the cell was increased due
119
to the gas released from the clathrates. The point where the clathrate dissociation line and the
120
thermal expansion line intersect was determined as the three-phase (clathrate (H) – liquid water
121
(LW) – vapor (V)) equilibrium point.
122
Gas uptake and composition measurements
123
The experiment for measuring gas uptake, which is the amount of gas consumed during clathrate
124
formation, was conducted under isobaric and isothermal conditions. The pressure of the cell was
125
maintained at 3.0 MPa, and the driving force (∆T), which is defined as the temperature
126
difference between experimental and equilibrium temperatures, was set to 5.0 K. A micro-flow
127
syringe pump (ISCO 500D; Teledyne Isco, Inc., USA) was used to maintain constant pressure
128
and to measure the gas volume consumed during clathrate formation. The volume of gas
129
supplemented into the cell at a constant pressure mode was recorded every 10 min for 2 h, and it
130
was then converted to the moles of gas consumed per moles of water charged for comparison of
131
gas uptakes for each promoter solution. Gas compositions during clathrate formation were
132
measured every 10 min using a gas chromatograph (GC, 7890A; Agilent, USA) with a thermal
133
conductivity detector (TCD) and a 80/100 Porapak Q Column (Supelco, USA). The vapor phase
134
was circulated between the cell and a sampling valve (Rheodyne, USA) with a loop of 20 µL
135
using a high-pressure metering pump (Eldex Laboratories, USA) to make a uniform composition
ACS Paragon Plus Environment
7
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 8 of 38
136
throughout the system. For the clathrate composition measurement, the cell was immersed in the
137
liquid nitrogen vessel for a short time period, and the vapor in the cell was then evacuated by a
138
vacuum pump (Rocker 300; GSS Scientific Co., USA) Clathrate compositions were measured
139
from the gas retrieved from clathrates at 298 K.
140
Spectroscopic analyses
141
A solid-state 400 MHz NMR spectrometer (Bruker, USA) that belongs to the Korea Basic
142
Science Institute (KBSI) was used to examine the structure and guest distributions of the
143
clathrates that were formed. The finely powdered clathrate samples were loaded into a 4 mm o.d.
144
Zr-rotor which was placed in a variable-temperature probe at 243 K. The 13C NMR spectra were
145
collected at a Larmor frequency of 100.6 MHz with magic angle spinning (MAS) from 2 to 4
146
kHz. The downfield carbon resonance peak of adamantane (38.3 ppm at 300 K) was used as an
147
external chemical shift reference.
148
An in situ fiber-coupled Raman spectrometer (SP550; Horiba, France) equipped with a
149
multichannel air cooled CCD detector and a 1,800 grooves/mm grating was used to confirm the
150
enclathration of guest molecules. The excitation source was a Nd:Yag laser emitting a 532 nm
151
line and providing 100 mW. Raman spectra were collected using a fiber-optic Raman probe that
152
was attached to the water-jacked cell. The clathrates were formed under isobaric (3.0 MPa) and
153
isothermal conditions. The driving force of ∆T = 5.0 K was given for each experiment. A more
154
detailed description of the experimental apparatus and methods were provided in our previous
155
papers13, 14, 19, 33.
ACS Paragon Plus Environment
8
Page 9 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
156
Results and Discussion
157
Thermodynamic stability and structure of clathrates
158
The three-phase (H-LW-V) equilibria of the CH4 (50%) + CO2 (50%) + promoter + water
159
systems at two different concentrations (1.0 mol% and stoichiometric concentrations of each
160
promoter clathrate) were measured in the pressure range of 0–7.0 MPa. The three-phase
161
equilibrium data were plotted in Figure 1 and listed in Table S1. THF and TBAC were used as
162
thermodynamic promoters to stabilize the CH4 (50%) + CO2 (50%) clathrate. The THF 5.6 mol%
163
corresponds to the stoichiometric concentration of THF·17.0H2O (sII clathrate), whereas the
164
TBAC 3.3 mol% corresponds to the stoichiometric concentration of TBAC·29.7H2O (semi-
165
clathrate)17, 37. The significant shift of the equilibrium curve to a higher temperature region at a
166
given pressure or to a lower pressure region at a given temperature indicates that the
167
thermodynamic stability of the CH4 + CO2 clathrate was significantly enhanced in the presence
168
of THF and TBAC. The extent of thermodynamic promotion was dependent on the concentration
169
of each promoter. Despite the significant thermodynamic promotion of both THF and TBAC for
170
the CH4 + CO2 clathrate, THF was a more effective thermodynamic promoter at a higher
171
pressure range, whereas TBAC showed higher thermodynamic stability at a lower pressure range
172
for both the 1.0 mol% and the stoichiometric concentration of each promoter. The clathrate phase
173
equilibria of CH4 + CO2 + promoter + water systems imply that promoter molecules (THF and
174
TBAC) are incorporated into the clathrate cages, and, thus, structural transformation of the
175
original CH4 + CO2 clathrate can occur due to the inclusion of the promoters.
176
13
177
in the clathrate cages.38. In particular, cage-dependent
C NMR spectroscopy is a powerful method to detect and quantify the carbon species captured 13
C NMR spectra of enclathrated CH4
ACS Paragon Plus Environment
9
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 10 of 38
178
molecules are effective in the identification of clathrate structure. The stacked plot of 13C MAS
179
NMR spectra of pure CH4, CH4 (50%) + CO2 (50%), CH4 (50%) + CO2 (50%) + THF (5.6
180
mol%), and CH4 (50%) + CO2 (50%) + TBAC (3.3 mol%) clathrates in the chemical shift range
181
of 0 to -10 ppm are depicted in Figure 2. The pure CH4 clathrate exhibited two resonance peaks
182
at -4.3 ppm and -6.6 ppm, which are assigned to CH4 molecules captured in the small 512 and
183
large 51262 cages of sI clathrate, respectively. The positions of NMR resonance peaks from the
184
CH4 (50%) + CO2 (50%) clathrate were identical to those from the pure CH4 clathrate, indicating
185
that the CH4 (50%) + CO2 (50%) clathrate is also sI. The area of each NMR resonance peak is
186
proportional to the number of CH4 molecules trapped in each clathrate cage. The theoretical peak
187
area ratio of CH4 molecules enclathrated in the large to small cages (AL/AS) for sI hydrate is 3.0
188
because the unit cell of sI hydrate consists of two small 512 and six large 51262 cages. The AL/AS
189
for the pure CH4 clathrate was found to be 3.3, which is very close to the theoretical ratio (3.0) of
190
sI. However, the AL/AS for the CH4 (50%) + CO2 (50%) clathrate was found to be 1.45, which is
191
relatively lower than that for the pure CH4 clathrate. This indicates that CO2 molecules were
192
preferentially captured in the large 51262 cages of the sI clathrate. On the other hand, the CH4
193
(50%) + CO2 (50%) + THF (5.6 mol%) clathrate had only one NMR resonance peak at -4.5 ppm
194
which can be assigned to the CH4 molecules enclathrated in the small 512 cages of sII. THF
195
molecules can occupy only large 51264 cages of sII, and at the stoichiometric concentration of 5.6
196
mol%, the large 51264 cages of sII are completely filled with THF molecules39. Therefore, CH4
197
molecules captured only in the small 512 cages of sII were detected at 4.5 ppm. The CH4 (50%) +
198
CO2 (50%) + TBAC (3.3 mol%) semi-clathrate had a resonance peak at -4.0 ppm which is also
199
assigned to CH4 molecules trapped in the small 512 cage of the semi-clathrate. In the pure TBAC
200
semi-clathrate, the large broken cages are occupied by TBA cations, whereas the small 512 cages
ACS Paragon Plus Environment
10
Page 11 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
201
are left vacant, which are then available for capturing CH4 molecules. Even though the small 512
202
cages are common for sI and sII clathrates and semi-clathrates, the slight shift in the resonance
203
peak position from CH4 molecules in the small 512 cages was observed because there is a slight
204
difference in the size and environment of the 512 cages in each structure40-42.
205
The enclathration of both CO2 and CH4 in the clathrate cages was identified by Raman
206
spectroscopy which is also useful in confirming the clathrate structure with various guests.
207
Figure 3 depicts Raman spectra of pure CH4, CH4 (50%) + CO2 (50%), CH4 (50%) + CO2 (50%)
208
+ THF (5.6 mol%), and CH4 (50%) + CO2 (50%) + TBAC (3.3 mol%) clathrates. The CH4
209
(50%) + CO2 (50%) clathrate exhibited two Raman peaks at 2,905 cm-1 and 2,915 cm-1 which
210
correspond to CH4 molecules captured in the large 51262 and small 512 cages of sI, and also two
211
Raman peaks at 1,276 cm-1 and 1,380 cm-1 which are attributed to CO2 molecules in the clathrate
212
cages43, 44. The Raman peak positions of each guest in the CH4 (50%) + CO2 (50%) clathrate
213
were identical with those in the pure CH4 and pure CO2 clathrates, confirming that the CH4
214
(50%) + CO2 (50%) clathrate is sI. However, the Raman peak of enclathrated CH4 molecules in
215
the CH4 (50%) + CO2 (50%) + THF (5.6 mol%) clathrate was detected only at 2,914 cm-1 which
216
can be assigned to the CH4 molecules in the small 512 cages of sII. The Raman peaks of
217
enclathrated CO2 molecules were observed at 1,274 cm-1 and 1,380 cm-1. In the CH4 (50%) +
218
CO2 (50%) + TBAC (3.3 mol%) semi-clathrate, one Raman peak for CH4 molecules captured in
219
the 512 cages appeared at 2,912 cm-1, and two Raman peaks for enclathrated CO2 molecules were
220
observed at 1,273 cm-1 and 1,380 cm-1, even though there were many broad Raman peaks that
221
emanated from the TBA cations captured in the semi-clathrates45. Raman spectra clearly
222
demonstrated that both CO2 and CH4 molecules are trapped in the clathrate cages and that the
ACS Paragon Plus Environment
11
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 12 of 38
223
corresponding Raman peak positions of each guest are slightly different depending on clathrate
224
structures.
225
Gas uptake and gas composition change during clathrate formation
226
The gas uptakes during clathrate formation were measured at 10 min intervals for the CH4 (50%)
227
+ CO2 (50%) gas mixture with pure water, THF, and TBAC solutions and shown in Figure 4.
228
The accumulated amount of gas consumption was expressed as moles of gas consumed per
229
moles of water charged. The gas uptake of the CH4 (50%) + CO2 (50%) + water system was
230
gradually increased during clathrate formation. The THF (5.6 mol%) solution showed a
231
relatively higher rate of clathrate growth than the pure water system in the early stage of hydrate
232
growth, but the final gas uptake of the THF (5.6 mol%) solution was smaller than that of the pure
233
water system. The TBAC solutions demonstrated lower gas consumption than other systems. The
234
amount of gas consumption during clathrate formation is closely related to the number of vacant
235
cages in the unit cell of each clathrate structure, as well as to the conversion of water into
236
clathrate. The unit cell of sI (pure water) and sII (THF solution) clathrates consists of 2(512)
237
·6(51262)·46H2O and 16(512) ·8(51264)·136H2O, respectively, and the TBAC solution forms a
238
semi-clathrate that has a tetragonal structure I (TS-I) with a unit cell of 4(51263) ·16(51262)
239
·10(512) ·172H2O17, 37, 46. At the stoichiometric concentration of each structure, the pure water
240
system has a higher ratio of the number of available cages to the number of water molecules in
241
the unit cell than the THF (5.6 mol%) solution system. For the THF (5.6 mol%) solution, only
242
small 512 cages of sII are available for capturing gas molecules because all of the large 51264
243
cages are occupied by THF molecules, whereas for the pure water system, both small and large
244
cages of sI can be used for enclathrating gas molecules. Therefore, the gas uptake of the pure
245
water system was higher than that of the THF (5.6 mol%) solution. The TBAC solution showed
ACS Paragon Plus Environment
12
Page 13 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
246
the lowest gas uptake due to the lowest ratio of the number of available cages to the number of
247
water molecules in the unit cell. Furthermore, the amount of gas consumption was also
248
dependent on the concentration of the promoters. The gas uptake for the THF (1.0 mol%) and
249
TBAC (1.0 mol%) solutions was significantly lower when compared to the solutions with the
250
stoichiometric concentration.
251
The growth rate of clathrate [mol/mol/min] was defined as moles of gas consumed for every 10
252
min per mole of charged water during the whole clathrate formation process (120 min) to
253
observe the growth patterns of the clathrates in each solution, and it is demonstrated in Figure
254
S1(a). The growth rate of clathrates formed from pure water was initially increased, then kept
255
almost constant until 60 min, and then, started to decrease. This indicates that the clathrates
256
without any promoters grow gradually. On the other hand, the growth rate of the clathrate
257
formed from the THF (5.6 mol%) solution reached the highest peak value in the first 20 min after
258
clathrate nucleation, and then started to decrease abruptly after 20 min. The THF (5.6 mol%)
259
solution demonstrated the relatively faster growth in the early stage of clathrate formation
260
compared to the pure water and THF (1.0 mol%) solution. The TBAC solutions generally
261
showed the lowest growth rate among all the solutions.
262
Furthermore, the normalized formation rate of clathrates for 30 min (NR30)7 is also depicted in
263
Figure S1(b). As can be expected from the gas uptakes (Figure 4) and the growth rate, NR30 of
264
the THF (5.6 mol%) solution was the highest and that of the TBAC (1.0 mol%) solution was the
265
lowest.
266
As gas molecules in the vapor phase are consumed by clathrate growth, the gas compositions in
267
the vapor phase change from the feed composition due to the different selectivity of guest gases
ACS Paragon Plus Environment
13
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 14 of 38
268
in the clathrate cages. CO2 composition changes in the vapor phase during clathrate formation
269
were measured every 10 min, and the results are displayed in Figure 5. The slight decline of the
270
CO2 concentration in the vapor phase before clathrate growth was observed due to high solubility
271
of CO2 in water. The CO2 composition changes in the vapor phase during clathrate formation can
272
be affected by the conversion of water into clathrate, CO2 selectivity in the clathrate phase, and
273
the ratio of head space volume to water volume in the reactor. The CO2 concentrations in the
274
vapor phase generally were decreased as the clathrate formation proceeded, except for the THF
275
(5.6 mol%) solution. For the pure water system, the CO2 concentration in the vapor phase was
276
gradually but most significantly decreased until 60 min because the CO2 is preferentially
277
captured in the clathrate cages. The final CO2 concentration in the vapor phase was found to be
278
∼35%. The TBAC (3.3 mol% and 1.0 mol%) solutions showed a very slight decrease of CO2
279
composition in the vapor phase and the final CO2 concentrations were ∼45% and ∼44%,
280
respectively. However, the THF (5.6 mol%) solution demonstrated the unusual behavior of an
281
increase in CO2 concentration in the vapor phase during clathrate formation, whereas the THF
282
(1.0 mol%) solution showed a decrease in CO2 concentration.
283
The CO2 compositions in the vapor and clathrate phases after completion of clathrate formation
284
are depicted in Figure 6. The pure water system demonstrated ∼56% CO2 in the clathrate phase,
285
whereas TBAC semi-clathrates produced significantly higher CO2 concentrations in the clathrate
286
phase (∼75% for 3.3 mol% and ∼72 % for 1.0 mol%). However, for the THF solutions, CO2
287
compositions in the clathrate phase were heavily dependent on the THF concentrations. The CO2
288
concentrations in the clathrate phase were found to be ∼45% and ∼66% for 5.6 mol% and 1.0
289
mol%, respectively. It should be noted from Figure 6 that for the THF (5.6 mol%) solution, CO2
290
is less selective than CH4 in the clathrate phase. That is why the CO2 concentration in the vapor
ACS Paragon Plus Environment
14
Page 15 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
291
phase continued to increase during clathrate formation, as shown in Figure 5. Even though the
292
gas uptakes of TBAC semi-clathrates were smaller than those of other systems, the CO2
293
selectivity in the clathrate phase was the highest and was not significantly dependent on the
294
TBAC concentrations.
295
The factors affecting CO2 selectivity in clathrates
296
For the CH4 + CO2 clathrates, CO2 selectivity in the clathrate phase can be affected primarily by
297
the thermodynamic stability of each clathrate formed by a single guest. As seen in Figure S2, the
298
pure CO2 clathrate is thermodynamically more stable than the pure CH4 clathrate, and it is so for
299
TBAC semi-clathrates as well33. Therefore, for pure water and TBAC solution systems, CO2 was
300
more preferentially captured in the clathrate phase than CH4 (Figure 5 and 6). However, the
301
thermodynamic stability of the CH4 + THF clathrates is generally higher than that of CO2 + THF
302
clathrates for both THF (1.0 and 5.6 mol%) solutions27,47,48, as seen in Figure S2, which indicates
303
that CH4 can be more selectively captured in the clathrate cages than CO2. For the THF (5.6
304
mol%) solution, it was actually observed that the CO2 concentration in the vapor phase was
305
increased during the clathrate formation and that the CO2 concentration in the clathrate phase
306
after completion of clathrate formation was lower than that in the vapor phase, which clearly
307
demonstrates preferential occupation of CH4 over CO2 in the clathrate phase.
308
For TBAC solutions, cage symmetry, as well as thermodynamic stability, can also affect CO2
309
selectivity in the semi-clathrate cages42, 49. QAS semi-clathrates possess two types of small
310
dodecahedral (D) cages (distorted D cages and regular D cages) which are available for trapping
311
CO2 and CH4 molecules. Due to the presence of distorted D cages, which have a strong
ACS Paragon Plus Environment
15
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 16 of 38
312
preference for CO2 molecules over CH4 molecules, CO2 selectivity in the TBAC semi-clathrates
313
was found to be higher compared to other clathrates.
314
For THF solutions, the cage filling behavior that depends on THF concentrations also exerts a
315
significant influence on CO2 selectivity in the clathrate phase. Guest distributions of CH4, CO2,
316
and THF molecules in the clathrates can be determined from NMR spectra shown in Figure 7.
317
The cage occupancy of each guest in the small and large cages of sI and sII clathrates can be
318
calculated through the following statistical thermodynamic equations by considering the area
319
ratios of each guest and the number of carbons in each guest molecule:
320
° ∆ߤ௪ = − ସ [6 ln(1 − ߠ,ுସ −ߠ,ைଶ ) + 2 ln(1 − ߠௌ,ுସ − ߠௌ,ைଶ)]
321
ோ்
° ∆ߤ௪ =−
ோ் ଵଷ
[8 ln(1 − ߠ,்ுி −ߠ,ுସ -ߠ,ைଶ ) + 16 ln(1 − ߠௌ,ுସ − ߠௌ,ைଶ)]
(1)
(2)
322
° ° where ∆ߤ௪ is the chemical potential of the empty lattice relative to clathrate cages (∆ߤ௪ =
323
ு ° ߤௐ − ߤௐ ), and ߠ, is the fractional cage occupancy of guest J in type i cage. The ∆ߤ௪ values
324
of 1,297 J/mol for Eq. (1) and 883.8 J/mol for Eq. (2) were used for sI and sII clathrates,
325
respectively 48,50,51. The occupancy ratios of ߠ,ுర /ߠௌ,ுర and ߠ,்ுி /ߠ௦,ுర were obtained from
326
the area ratios shown in Figure 7, and the composition ratio of CH4 to CO2 in the clathrate phase
327
was obtained by GC measurement and the assumption of large cage occupancy50. The calculated
328
cage occupancy of each guest for the pure water and THF (5.6 mol%) solution systems is listed
329
in Table 1 along with predicted values determined by CSMGem software17. For the pure water
330
system, the estimated cage occupancy of CO2 in the large 51262 cages (0.669) was larger than that
331
of CH4 (0.311), and the cage occupancy of CO2 in the small 512 cages (0.100) was much lower
332
than that of CH4 (0.655). It indicates that CO2 preferred to occupy the large 51262 cages of sI,
ఉ
ACS Paragon Plus Environment
16
Page 17 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
333
whereas CH4 predominantly occupied the small 512 cages of sI. The relative cage occupancy
334
ratio of THF in the large 51264 cages to CH4 in the small 512 cages (ߠ,்ுி /ߠ௦,ுర ) in the 5.6
335
mol% THF clathrate was found to be 2.88, whereas that in the 1.0 mol% THF clathrate was 1.29.
336
At the stoichiometric concentration (5.6 mol%), THF molecules fully occupy the large 51264
337
cages of sII, whereas, at THF concentrations lower than 5.6 mol%, gas molecules can also
338
occupy the large 51264 cages, which is called “tuning behavior”
339
ߠ,்ுி /ߠ௦,ுర at 1.0 mol% THF indicates that CO2 molecules preferentially occupied the large
340
51264 cages, thereby resulting in a higher CO2 concentration in the clathrate phase at 1.0 mol%
341
THF.
342
In this study, clathrate-based CO2 capture was investigated for upgrading CO2-rich natural gas
343
and biogas. The phase equilibria, gas uptakes, gas composition measurements, and spectroscopic
344
analyses of CH4 (50%) + CO2 (50%) + promoter clathrates were examined to elucidate the effects
345
of thermodynamic promoters (THF and TBAC) on clathrate stability and cage filling behavior.
346
The addition of both THF and TBAC resulted in a significant thermodynamic promotion, which
347
was dependent on the promoter concentrations. The pure water and THF solutions demonstrated
348
higher gas uptakes and faster growth rates than TBAC solutions, which is attributed to the higher
349
and faster conversion of water into clathrate, as well as the larger number of available cages in
350
the unit cell of the clathrates formed. However, TBAC solutions gave higher CO2 selectivity in
351
the clathrate phase due to the presence of distorted D cages in the semi-clathrate structure which
352
have a strong preference for CO2 molecules over CH4 molecules. For the THF (5.6 mol%)
353
solution, the CO2 concentration in the vapor phase continued to increase during clathrate
354
formation, and the CO2 concentration in the clathrate phase after completion of clathrate
355
formation was found to be lower than that of feed gas because of the lower thermodynamic
39, 52
. The lower ratio of
ACS Paragon Plus Environment
17
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 18 of 38
356
stability of CO2+THF clathrates compared to CH4 +THF clathrates and the full occupancy of
357
THF molecules in the large 51264 cages of sII. The CO2 selectivity of the THF (1.0 mol%)
358
solution was higher than that of the THF (5.6 mol%) solution because CO2 can also occupy the
359
large 51264 cages of sII. However, the CO2 selectivity of TBAC solutions was not significantly
360
dependent on TBAC concentrations. The overall experimental results demonstrated that
361
thermodynamic stability, cage shape and dimension, and cage filling behavior can affect CO2
362
selectivity in each clathrate phase. THF solutions produced higher gas uptakes and faster growth
363
rates for clathrates, but lower CO2 selectivity in the clathrate phase, whereas TBAC solutions
364
demonstrated lower gas uptakes, but higher CO2 selectivity. It should also be noted that THF is
365
volatile and toxic, whereas TBAC is non-volatile and reusable. Therefore, TBAC would be one
366
of the efficient thermodynamic promoters to separate CO2, and careful consideration should be
367
given to the selection of a suitable promoter and its optimum concentration in designing and
368
operating clathrate-based CO2 capture from sour natural gas or biogas.
369
Corresponding Author
370
* Tel: +82-52-217-2821. Fax: +82-52-217-2859. E-mail:
[email protected].
371
Notes
372
The authors declare no competing financial interest.
373
ACKNOWLEDGMENT
374
This research was supported by the National Research Foundation of Korea (NRF) grant funded
375
by the Ministry of Education (2016R1D1A1A02937037) and also by the Korea Institute of
376
Energy Technology Evaluation and Planning (KETEP) through "Human Resources Program in
ACS Paragon Plus Environment
18
Page 19 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
377
Energy Technology" (No. 20164030201010) funded by the Ministry of Trade, Industry and
378
Energy, Republic of Korea.
ACS Paragon Plus Environment
19
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
379
Page 20 of 38
REFERENCES
380
(1) Zhang, D.; Chen, Y.; Zhao, Y.; Zhu, X., New sludge pretreatment method to improve
381
methane production in waste activated sludge digestion. Environ. Sci. Technol. 2010, 44,
382
4802-4808.
383
(2) Jaramillo, P.; Griffin, W. M.; Matthews, H. S., Comparative life-cycle air emissions of
384
coal, domestic natural gas, LNG, and SNG for electricity generation. Environ. Sci. Technol.
385
2007, 41, 6290-6296.
386
(3) Wasiu, A. B.; Aziz, A. R.; Heikal, M. R., The Effect of Carbon Dioxide Content-natural
387
Gas on the Performance Characteristics of Engines: A Review. J. Appl. Sci. 2012, 12, 2346-
388
2350.
389
(4) Cho, J. D., Global Trends of Sciences Information on the Sour Gas. Economic and
390
Environmental Geology 2015, 48, 89-101.
391
(5) Andriani, D.; Wresta, A.; Atmaja, T. D.; Saepudin, A., A review on optimization
392
production and upgrading biogas through CO2 removal using various techniques. Appl.
393
Biochem. Biotechnol. 2014, 172, 1909-1928.
394
(6) Mondal, M. K.; Balsora, H. K.; Varshney, P., Progress and trends in CO2
395
capture/separation technologies: a review. Energy 2012, 46, 431-441.
396
(7) Babu, P.; Linga, P.; Kumar, R.; Englezos, P., A review of the hydrate based gas
397
separation (HBGS) process for carbon dioxide pre-combustion capture. Energy 2015, 85,
398
261-279.
ACS Paragon Plus Environment
20
Page 21 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
399
(8) Eslamimanesh, A.;
Mohammadi, A. H.; Richon, D.; Naidoo, P.; Ramjugernath, D.,
400
Application of gas hydrate formation in separation processes: a review of experimental
401
studies. J. Chem. Thermodyn. 2012, 46, 62-71.
402
(9) Kamata, Y.; Yamakoshi, Y.; Ebinuma, T.; Oyama, H.; Shimada, W.; Narita, H.,
403
Hydrogen sulfide separation using tetra-n-butyl ammonium bromide semi-clathrate (TBAB)
404
hydrate. Energy Fuels 2005, 19, 1717-1722.
405
(10) Yang, M.; Song, Y.; Jiang, L.; Zhao, Y.; Ruan, X.; Zhang, Y.; Wang, S., Hydrate-based
406
technology for CO2 capture from fossil fuel power plants. Appl. Energy 2014, 116, 26-40.
407
(11) Kim, E.; Ko, G.; Seo, Y., Greenhouse gas (CHF3) separation by gas hydrate formation.
408
ACS Sustainable Chem. Eng. 2017, 5, 5485–5492.
409
(12) Herslund, P. J.; Thomsen, K.; Abildskov, J.; von Solms, N., Modelling of
410
tetrahydrofuran promoted gas hydrate systems for carbon dioxide capture processes. Fluid
411
Phase Equilib. 2014, 375, 45-65.
412
(13) Park, S.; Lee, S.; Lee, Y.; Seo, Y., CO2 capture from simulated fuel gas mixtures using
413
semiclathrate hydrates formed by quaternary ammonium salts. Environ. Sci. Technol. 2013,
414
47(13):7571-7577.
415
(14) Cha, I.; Lee, S.; Lee, J. D.; Lee, G. W.; Seo, Y., Separation of SF6 from gas mixtures
416
using gas hydrate formation. Environ. Sci. Technol. 2010, 44, 6117-6122.
ACS Paragon Plus Environment
21
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 22 of 38
417
(15) Bhattacharjee, G.; Kumar, A.; Sakpal, T.; Kumar, R., Carbon dioxide sequestration:
418
influence of porous media on hydrate formation kinetics. ACS Sustainable Chem. Eng. 2015,
419
3, 1205-1214.
420
(16) Di Profio, P.; Canale, V.; D’Alessandro, N.; Germani, R.; Di Crescenzo, A.; Fontana,
421
A., Separation of CO2 and CH4 from Biogas by Formation of Clathrate Hydrates: Importance
422
of the Driving Force and Kinetic Promoters. ACS Sustainable Chem. Eng. 2017, 5, 1990-
423
1997.
424
(17) Sloan, E. D.; Koh, C. A., Clathrate Hydrates of Natural Gases. 3rd ed.; CRC
425
Press/Taylor & Francis: Boca Raton, 2008.
426
(18) Koh, C. A.; Sum, A. K.; Sloan, E. D., State of the art: Natural gas hydrates as a natural
427
resource. J. Nat. Gas Sci. Eng. 2012, 8, 132-138.
428
(19) Kim, S.; Seo, Y., Semiclathrate-based CO2 capture from flue gas mixtures: An
429
experimental approach with thermodynamic and Raman spectroscopic analyses. Appl.
430
Energy 2015, 154, 987-994.
431
(20) Aladko, L. S.; Dyadin, Y. A.; Rodionova, T. V.; Terekhova, I. S., Clathrate hydrates of
432
tetrabutylammonium and tetraisoamylammonium halides. J. Struct. Chem. 2002, 43, 990-
433
994.
434
(21) Fukumoto, A.; Paricaud, P.; Dalmazzone, D.; Bouchafaa, W.; Ho, T. T.; Fürst, W.,
435
Modeling the dissociation conditions of carbon dioxide+ TBAB, TBAC, TBAF, and TBPB
436
semiclathrate hydrates. J. Chem. Eng. Data 2014, 59, 3193-3204.
ACS Paragon Plus Environment
22
Page 23 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
437
(22) Iino K.; Sakakibara Y.; Suginaka T.; Ohmura R., Phase equilibria for the ionic
438
semiclathrate hydrate formed with tetrabutylphosphonium chloride plus CO2, CH4, or N2. J.
439
Chem. Thermodyn. 2014, 71, 133-136.
440
(23) Yang, S., Natural Gas Physical Properties Under High Pressure. In Fundamentals of
441
Petrophysics. Springer Berlin Heidelberg 2017; pp 27-74.
442
(24) Iino K.; Takeya S.; Ohmura R., Characterization of clathrate hydrates formed with CH4
443
or CO2 plus tetrahydropyran. Fuel 2014, 122, 270-276.
444
(25) Zhang, B.; Wu, Q., Thermodynamic promotion of tetrahydrofuran on methane
445
separation from low-concentration coal mine methane based on hydrate. Energy Fuels 2010,
446
24, 2530-2535.
447
(26) Veluswamy, H. P.; Kumar, S.; Kumar, R.; Rangsunvigit, P.; Linga, P., Enhanced
448
clathrate hydrate formation kinetics at near ambient temperatures and moderate pressures:
449
Application to natural gas storage. Fuel 2016, 182, 907-919.
450
(27) Lee, Y. J.; Kawamura, T.; Yamamoto, Y.; Yoon, J. H., Phase equilibrium studies of
451
tetrahydrofuran (THF) + CH4, THF + CO2, CH4 + CO2, and THF + CO2 + CH4 hydrates. J.
452
Chem. Eng. Data 2012, 57, 3543-3548.
453
(28) Chapoy, A.; Anderson, R.; Tohidi, B.; Low-pressure molecular hydrogen storage in
454
semi-clathrate hydrates of quaternary ammonium compounds. J. Am. Chem. Soc. 2007, 129,
455
746-747.
ACS Paragon Plus Environment
23
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 24 of 38
456
(29) Ogata, K.; Tsuda, T.; Amano, S.; Hashimoto, S.; Sugahara, T.; Ohgaki, K.; Hydrogen
457
storage in trimethylamine hydrate: Thermodynamic stability and hydrogen storage capacity
458
of hydrogen + trimethylamine mixed semi-clathrate hydrate. Chem. Eng. Sci. 2010, 65, 1616-
459
1620.
460
(30) Sun, Q.; Guo, X.; Liu, A.; Liu, B.; Huo, Y.; Chen, G., Experimental study on the
461
separation of CH4 and N2 via hydrate formation in TBAB solution. Ind. Eng. Chem. Res.
462
2010, 50, 2284-2288.
463
(31) Yang, M.; Jing, W.; Zhao, J.; Ling, Z.; Song, Y., Promotion of hydrate-based CO2
464
capture from flue gas by additive mixtures (THF (tetrahydrofuran) + TBAB (tetra-n-butyl
465
ammonium bromide)). Energy 2016, 106, 546-553.
466
(32) Babu, P.; Chin, W. I.; Kumar, R.; Linga, P., Systematic evaluation of tetra-n-butyl
467
ammonium bromide (TBAB) for carbon dioxide capture employing the clathrate process.
468
Ind. Eng. Chem. Res. 2014, 53, 4878-4887.
469
(33) Kim, S.; Baek, I. H.; You, J. K.; Seo, Y., Guest gas enclathration in tetra-n-butyl
470
ammonium chloride (TBAC) semiclathrates: potential application to natural gas storage and
471
CO2 capture. Appl. Energy 2015, 140, 107-112.
472
(34) Fan, S.; Li, S.; Wang, J.; Lang, X.; Wang, Y., Efficient capture of CO2 from simulated
473
flue gas by formation of TBAB or TBAF semiclathrate hydrates. Energy Fuels 2009, 23,
474
4202-4208.
ACS Paragon Plus Environment
24
Page 25 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
475
(35) Tomita S.; Akatsu S.; Ohmura R., Experiments and thermodynamic simulations for
476
continuous separation of CO2 from CH4+ CO2 gas mixture utilizing hydrate formation. Appl.
477
Energy 2015, 146, 104-110.
478
(36) Uchida T.; Ikeda I. Y.; Takeya S.; Kamata Y.; Ohmura R.; Nagao J.; Zatsepina O. Y.;
479
Buffett B. A., Kinetics and Stability of CH4–CO2 Mixed Gas Hydrates during Formation and
480
Long‐Term Storage. ChemPhysChem 2005, 6, 646-654.
481
(37) Rodionova, T.; Komarov, V.; Villevald, G.; Aladko, L.; Karpova, T.; Manakov, A.,
482
Calorimetric and structural studies of tetrabutylammonium chloride ionic clathrate hydrates.
483
J. Phys. Chem. B 2010, 114, 11838-11846.
484
(38) Ripmeester, J. A.; Ratcliffe, C. I., On the contributions of NMR spectroscopy to
485
clathrate science. J. Struct. Chem. 1999, 40, 654-662.
486
(39) Seo, Y.; Lee, J. W.; Kumar, R.; Moudrakovski, I. L.; Lee, H.; Ripmeester, J. A., Tuning
487
the composition of guest molecules in clathrate hydrates: NMR identification and its
488
significance to gas storage. Chemistry–An Asian Journal 2009, 4, 1266-1274.
489
(40) Lee, S.; Lee, Y.; Park, S.; Kim, Y.; Lee, J. D.; Seo, Y., Thermodynamic and
490
spectroscopic identification of guest gas enclathration in the double tetra-n-butylammonium
491
fluoride semiclathrates. J. Phys. Chem. B 2012, 116, 9075-9081.
492
(41) Pavia, D. L.; Lampman, G. M.; Kriz, G. S.; Vyvyan, J. A., Introduction to spectroscopy.
493
Cengage Learning, 2008.
ACS Paragon Plus Environment
25
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 26 of 38
494
(42) Muromachi, S.; Takeya, S.; Yamamoto, Y.; Ohmura, R., Characterization of tetra-n-
495
butylphosphonium bromide semiclathrate hydrate by crystal structure analysis. Cryst. Eng.
496
Comm. 2014, 16, 2056-2060.
497
(43) Chen, L.; Lu, H.; Ripmeester, J. A., Raman spectroscopic study of CO2 in hydrate cages.
498
Chem. Eng. Sci. 2015, 138, 706-711.
499
(44) Sum, A. K.; Burruss, R. C.; Sloan, E. D., Measurement of clathrate hydrates via Raman
500
spectroscopy. J. Phys. Chem. B 1997, 101, 7371-7377.
501
(45) Chazallon, B.; Ziskind, M.; Carpentier, Y.; Focsa, C., CO2 capture using semi-clathrates
502
of quaternary ammonium salt: structure change induced by CO2 and N2 enclathration. J.
503
Phys. Chem. B 2014, 118, 13440-13452.
504
(46) Terekhova, I. S.; Manakov, A. Y.; Komarov, V. Y.; Villevald, G. V.; Burdin, A. A.;
505
Karpova, T. D.; Aladko, E. Y., Physicochemical and Structural Studies of Clathrate Hydrates
506
of Tetrabutylammonium Polyacrylates. J. Phys. Chem. B 2013, 117, 2796-2806.
507
(47) Mohammadi, A. H.; Richon, D., Phase equilibria of clathrate hydrates of tetrahydrofuran
508
+ hydrogen sulfide and tetrahydrofuran + methane. Ind. Eng. Chem. Res. 2009, 48, 7838-
509
7841.
510
(48) Seo, Y.; Kang, S. P.; Lee, S.; Lee, H., Experimental measurements of hydrate phase
511
equilibria for carbon dioxide in the presence of THF, propylene oxide, and 1, 4-dioxane. J.
512
Chem. Eng. Data 2008, 53, 2833-2837.
ACS Paragon Plus Environment
26
Page 27 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
513
(49) Muromachi, S.; Udachin, K. A.; Shin, K.; Alavi, S.; Moudrakovski, I. L.; Ohmura, R.;
514
Ripmeester, J. A., Guest-induced symmetry lowering of an ionic clathrate material for carbon
515
capture. Chem. Commun. 2014, 50, 11476-11479.
516
(50) Seol, J.; Lee, J. W.; Kim, D. Y.; Takeya, S.; Ripmeester, J. A.; Lee, H., Molecular Cage
517
Occupancy of Clathrate Hydrates at Infinite Dilution: Experimental Determination and
518
Thermodynamic Significance. J. Phys. Chem. B 2009, 114, 804-808.
519
(51) Seo, Y. T.; Lee, H., 13C NMR analysis and gas uptake measurements of pure and mixed
520
gas hydrates: development of natural gas transport and storage method using gas hydrate.
521
Korean J. Chem. Eng. 2003, 20, 1085-1091.
522
(52) Kim, D. Y.; Park, J.; Lee, J. W.; Ripmeester, J. A.; Lee, H., Critical guest concentration
523
and complete tuning pattern appearing in the binary clathrate hydrates. J. Am. Chem. Soc.
524
2006, 128, 15360-15361.
ACS Paragon Plus Environment
27
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
525
Page 28 of 38
FIGURE CAPTION
526
Figure 1. Clathrate phase equilibria of the CH4 (50%) + CO2 (50%) + promoter + water
527
systems.
528
Figure 2. 13C NMR spectra of pure CH4, CH4 (50%) + CO2 (50%), CH4 (50%) + CO2 (50%)
529
+ THF (5.6 mol%), and CH4 (50%) + CO2 (50%) + TBAC (3.3 mol%) clathrates
530
Figure 3. Raman spectra of pure CH4, CH4 (50%) + CO2 (50%), CH4 (50%) + CO2 (50%) +
531
THF (5.6 mol%), and CH4 (50%) + CO2 (50%) + TBAC (3.3 mol%) clathrates
532
Figure 4. Gas uptakes of the CH4 (50%) + CO2 (50%) + promoter + water systems during
533
clathrate formation at 3.0 MPa and ∆T = 5.0 K.
534
Figure 5. CO2 concentration changes in the vapor phase during the clathrate formation.
535
Figure 6. CO2 compositions in the vapor and clathrate phases after completion of clathrate
536
formation.
537
Figure 7.
538
(5.6 mol%), and CH4 (50%) + CO2 (50%) + THF (1.0 mol%) clathrates.
13
C NMR Spectra of CH4 (50%) + CO2 (50%), CH4 (50%) + CO2 (50%) + THF
ACS Paragon Plus Environment
28
Page 29 of 38
8 pure w ater
7
THF 5.6 mol% THF 1.0 mol% TBAC 3.3 mol% TBAC 1.0 mol%
6
Pressure (MPa)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
5
4
3
2
1
0 270
280
285
290
295
300
Temperature (K)
539 540
275
Figure 1.
ACS Paragon Plus Environment
29
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 30 of 38
-6.6
-4.3
pure CH4 clathrate (sI) -6.6 -4.3
CH4 (50%) + CO2 (50%) clathrate (sI) -4.5
CH4 (50%) + CO2 (50%) + THF (5.6 mol%) clathrate (sII) -4.0
CH4 (50%) + CO2 (50%) + TBAC (3.3 mol%) semi-clathrate
0
-4
-6
-8
-10
Chemical Shift (ppm)
541 542
-2
Figure 2.
ACS Paragon Plus Environment
30
Page 31 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
2905
2915
pure CH4 clathrate (sI) 2905
2915
1380 1276
CH4 (50%) + CO2 (50%) clathrate (sI) 2914
1380
1274
CH4 (50%) + CO2 (50%) + THF (5.6 mol%) clathrate (sII) 2912
1380
1273
CH4 (50%) + CO2 (50%) + TBAC (3.3 mol%) semi-clathrate
1200
1400
1500 2850
2900
2950
3000
-1
Wavenumber (cm )
543 544
1300
Figure 3.
ACS Paragon Plus Environment
31
ACS Sustainable Chemistry & Engineering
0.12 pure water
Consumed mol of gas per mol of water (mol/mol)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 32 of 38
THF 5.6 mol% THF 1.0 mol% TBAC 3.3 mol% TBAC 1.0 mol%
0.10
0.08
0.06
0.04
0.02
0.00 0
20
40
60
80
100
120
Time (min)
545 546
Figure 4.
ACS Paragon Plus Environment
32
Page 33 of 38
55
CO2 concentration in the vapor phase (%)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
50
45
40
pure water THF 5.6 mol% THF 1.0 mol% TBAC 3.3 mol% TBAC 1.0 mol%
35
30 0
40
60
80
100
120
Time (min)
547 548
20
Figure 5.
ACS Paragon Plus Environment
33
ACS Sustainable Chemistry & Engineering
100 90
vapor phase clathrate phase
80
CO2 composition (%)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 34 of 38
70 60 50 40 30 20 10 0
pure water
THF 5.6 mol%
THF 1.0 mol%
TBAC 3.3 mol%
TBAC 1.0 mol%
549 550
Figure 6.
ACS Paragon Plus Environment
34
Page 35 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
CH4 in sI-L - 6.6 CH4 in sI-s - 4.3
CH4 (50%) + CO2 (50%) clathrate (sI)
THF in sII-L 25.9
THF in sII-L 67.9
CH4 in sII-s - 4.5
CH4 (50%) + CO2 (50%) + THF (5.6 mol%) clathrate (sII) THF in sII-L 25.9
THF in sII-L 67.9
CH4 in sII-s - 4.5
CH4 (50%) + CO2 (50%) + THF (1.0 mol%) clathrate (sII)
80
40
20
0
-20
Chemical Shift (ppm)
551 552
60
Figure 7.
ACS Paragon Plus Environment
35
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
553
Page 36 of 38
Table 1. Cage occupancy of each guest molecule in the clathrate cages.
Large cage
Small cage system
ߠ௦, ுସ
ߠ௦, ைଶ
Pure water
0.655
0.100
Pure water (CSMGem)
0.598
THF (5.6 mol%)
0.344
ߠ௦,
ࣂࡿ,࢚࢚ࢇ
ߠ, ுସ
ߠ, ைଶ
ߠ, ்ுி
ࣂࡸ,࢚࢚ࢇ
-
0.753
0.311
0.669
-
0.980
0.187
-
0.785
0.326
0.637
-
0.963
0.270
-
0.614
-
-
0.990
0.990
்ுி
554
ACS Paragon Plus Environment
36
Page 37 of 38 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
555
Supporting Information. Figures of growth rate of the CH4 (50%) + CO2 (50%) + promoter +
556
water systems, normalized growth rate for 30 min (NR30) of the CH4 (50%) + CO2 (50%) +
557
promoter + water systems, and phase equilibria of CO2 and CH4 clathrates in THF 5.6 mol% and
558
1.0 mol% systems and Table of clathrate phase equilibrium data of the CH4 (50%) + CO2 (50%)
559
+ promoter + water systems.
ACS Paragon Plus Environment
37
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 38 of 38
560
Synopsis
561
Clathrate-based CO2 capture was investigated in the presence of thermodynamic promoters for
562
upgrading CO2-rich natural gas and biogas.
563
TOC/Abstract Art
564
ACS Paragon Plus Environment
38