
Web Release Date: February 19,
Designing Adsorbents for CO2 Capture from Flue Gas-Hyperbranched Aminosilicas Capable of Capturing CO2 Reversibly




and

School of Chemical & Biomolecular Engineering, Georgia Institute of Technology, 311 Ferst Drive, Atlanta, Georgia 30332, and U.S. Department of Energy, National Energy Technology Laboratory, 626 Cochrans Mill Road, Pittsburgh, Pennsylvania 15236
Received October 10, 2007
Abstract:
Carbon dioxide adsorption from a simulated flue gas stream was successfully performed with a hyperbranched aminosilica (HAS) material. The HAS was synthesized by a one-step reaction, spontaneous aziridine ring-opening polymerization off of surface silanols, to form a 32 wt % organic/inorganic hybrid material. The adsorption measurements were performed in a fixed-bed flow reactor using humidified CO2. The advantage of this adsorbent over previously reported adsorbents is the stability of the organic groups covalently bound to the silica support compared to those made by physisorbed methods. Furthermore, a large CO2 capacity (~3 mmol CO2/g adsorbent) associated with the high loading of amines was observed.
Due to the increasing CO2 concentration in the atmosphere,
contemporary research has focused on ways to slow or stop this
trend. CO2 capture has attracted attention due to the potential to
trap and sequester large amounts of CO2 from concentrated sources
such as power plants. Traditional technologies in capturing CO2
include absorption by aqueous amines.1 However, utilization of this
process is energy intensive and expensive when used for large
volumes of dilute gas, such as flue gas.2 This is primarily due to
the high heat capacity of water and use of temperature swings to
induce CO2 desorption. Many types of amine-modified silica
materials have been reported (e.g., amine-tethered silica materials,3
amines impregnated into porous silicas,4,5
| Scheme 1. Solid CO2 Adsorbents |
The synthesis of HAS was performed via a one-step reaction between aziridine and the silica surface.6 As previously reported on silica wafers, the surface silanols initiated aziridine polymerization off the surface.6 Due to low surface areas, hybrid aminosilica materials constructed on silica wafers are impractical adsorbents. However, the formation of hybrid aminosilicas on high surface area mesoporous silica materials7,8 can lead to materials capable of reversibly binding CO2 with substantial capacities (>2 mmol CO2/g). The aziridine monomer was added to SBA-15 dispersed in a toluene solution with catalytic amounts of acetic acid and stirred at room temperature in a glass pressure reaction vessel. The resulting HAS material (SBA-HA) was washed extensively to remove physisorbed aziridine or unbound oligomer from the surface. The organic loading of the grafted hybrid aminosilica used here was determined via elemental analysis as 7.0 mmol N/g material.
For these studies, the hybrid aminosilica was uniformly dispersed
in sand and tested in a fixed bed flow system. The adsorbent/sand
mixture allowed for decreased heat effects and reproducible flow
through the bed. The SBA-HA material was analyzed for CO2
capture at 25
C and 75
C with 10% CO2/Ar saturated with water
flowing at a rate of 20 mL/min. The adsorption of CO2 on the
aminosilica was determined by monitoring the effluent gas with a
mass spectrometer. After the adsorption experiment, the gas was
switched to pure argon, and the CO2 was desorbed from the surface
at 130
C for at least 3 h. As shown in Figure 1, the SBA-HA
material captured CO2 reversibly in all 11 experiments performed
with an average capacity of 1.98 mmol CO2/g adsorbent (6.6 mmol
CO2/g aziridine monomer or 0.28 mmol CO2/mmol N).9 The CO2
adsorption capacities were found to be relatively constant, ranging
between 1.9 and 2.1 mmol CO2/g. Hence, under simulated flue gas
conditions, the SBA-HA material demonstrated promising CO2
adsorption properties.
Figure 1 Multicycle CO2 testing of SBA-HA at 75 C.
|
Additionally, the SBA-HA material reported in the literature was
compared to a number of the best materials (Scheme 1). For
instance, traditionally functionalized (SBA-NH2)10 and diamine-functionalized (SBA-diamine) aminosilicas were synthesized with
amine loadings of 1.9 mmol N/g and 2.5 mmol N/g, respectively.
When analyzed in the fixed bed flow system, these materials
captured CO2 with capacities of approximately 10% (SBA-NH2)
and 20% (SBA-diamine) that of the SBA-HA material at 25
C
(Table 1
). The high loading of amines on the hybrid aminosilica
(SBA-HA) allowed for a CO2 capacity of 3.1 mmol CO2/g at 25
C, which is the basis for the data in Table 1.
Three additional materials were synthesized via impregnation
of (i) a high molecular weight PEI4 into calcined SBA-15 (SBA/PEI(750 000 MW)), (ii) a low molecular weight PEI into calcined SBA-15 (SBA/PEI(800 MW)),4 or (iii) tetraethylenepentamine (TEPA) into
uncalcined SBA-155 (SBA-UCTEPA). The SBA/PEI(750 000 MW)
material captured approximately 70% as much CO2 per gram
adsorbent as the SBA-HA material. Similar to previous reports,4
the capacities of the SBA/PEI materials increased at a higher
temperature, possibly due to swelling of the amine polymer within
the porous support. However, when SBA/PEI(800 MW) was studied,
the capacities were not reproducible due to the texture of the
material. When the PEI was impregnated in the SBA-15, the
resulting material was very "sticky" due to the addition of the PEI
polymer to the internal and external surface of the SBA-15.
Furthermore, these materials typically clogged the adsorption
column, creating a significant decrease in the volumetric flow rate
and a large pressure drop. Thus, CO2 adsorption capacities with
these materials could not be determined in our system. The sample
prepared by impregnation of TEPA into uncalcined SBA-15 (SBA-UCTEPA) captured CO2 with high capacities at 75
C. However,
a decrease in CO2 capacity was observed after subsequent runs (see
the Supporting Information), likely due to leaching of the physisorbed TEPA from the support. Furthermore, at lower temperatures,
the capacity decreased substantially (Table 1). Although high amine
loadings can be obtained by physically adsorbing low molecular
weight amines onto the support material, the longevity of such a
material appears limited due to leaching of the organics from the
support.
The easy to synthesize, robust HAS material is capable of
adsorbing CO2 reversibly with very high capacities of 3.1 mmol
CO2/g material at 25
C. The advantage of this adsorbent over
previously reported adsorbents rests in its large CO2 capacity and
demonstrated multicycle stability. The material was recycled by
thermally desorbing the CO2 from the surface with essentially no
changes in capacity. Furthermore, the organic groups on the surface
were stable in the temperature range between 25 and 130
C due
to the covalent attachment between the support and the organic
groups. We report the first use of hybrid aminosilicas of this type
for CO2 capture. Based on the high amine loading, the ability to
recycle the materials, and the high CO2 affinity, these materials
are very promising new materials for acid gas capture from flue
gas streams.
This work was fully supported by the U.S. Department of Energy, National Energy Technology Laboratory under contract no. 41817M3226.
Control material adsorption testing, experimental methods, XRD, FT-Raman spectra, CPMAS 13C NMR spectra, porosity data, and polymer characterization. This material is available free of charge via the Internet at http://pubs.acs.org.
* In papers with more than one author, the asterisk indicates the name of the author to whom inquiries about the paper should be addressed.
Georgia Institute of Technology.
U.S. Department of Energy.
1. Astarita, G. Chem. Eng. Sci. 1961, 16, 202.
2. Huang, H. Y.; Chinn, D.; Munson, C. L.; Yang, R. T. Ind. Eng. Chem.
Res. 2003, 42, 2427.
3. (a) Tsuda, T.; Tsuyoshi, F. J. Chem. Soc., Chem. Commun. 1992, 1659.
(b) Leal, O.; Bolivar, C.; Ovalles, C.; Garcia, J. J.; Espidel, Y. Inorg.
Chim. Acta 1995, 240, 183.
(c) Gray, M. L.; Soong, Y.; Champagne, K.
J.; Pennline, H. W.; Baltrus, J.; Stevens, R. W., Jr.; Khatri, R.; Chuang,
S. S. C. Int. J. Environ. Technol. Manage. 2004, 4, 82.
(d) Gray, M. L.;
Soong, Y.; Champagne, K. J.; Pennline, H. W.; Baltrus, J.; Stevens, R.
W., Jr.; Khatri, R.; Chuang, S. S. C.; Filburn, T. Fuel Proc. Technol.
2005, 86, 1449.
(e) Khatri, R. A.; Chuang, S. S. C.; Soong, Y.; Gray, M.
Energy Fuels 2006, 20, 1514.
(f) Kim, S.; Ida, J.; Guliants, V. V.; Lin, J.
Y. S. J. Phys. Chem. B 2005, 109, 6287.
(g) Knowles, G. P.; Graham, J.
V.; Delaney, S. W.; Chaffee, A. L. Fuel Proc. Technol. 2005, 86, 1435.
(h) Chang, A. C. C.; Chuang, S. S. C.; Gray, M.; Soong, Y. Energy Fuels
2003, 17, 468.
(i) Zheng, F.; Tran, D. N.; Busche, B. J.; Fryxell, G. E.;
Addlemann, R. S.; Zemanian, T. S.; Aardahl, C. L. Ind. Eng. Chem. Res.
2005, 44, 3099.
(j) Khatri, R. A.; Chuang, S. S. C.; Soong, Y.; Gray, M.
Ind. Eng. Chem. Res. 2005, 44, 3702.
(k) Harlick, P. J. E.; Sayari, A. Ind.
Eng. Chem. Res. 2007, 46, 446.
(l) Harlick, P. J. E.; Sayari, A. Ind. Eng.
Chem. Res. 2006, 45, 3248.
(m) Knowles, G. P.; Delaney, S. W.; Chaffee,
A. L. Ind. Eng. Chem. Res. 2006, 45, 2626.
4. (a) Xu, X.; Song, C.; Andresen, J. M.; Miller, B. G.; Scaroni, A. W.
Microporous Mesoporous Mater. 2003, 62, 29.
(b) Xu, X.; Song, C.;
Andresen, J. M.; Miller, B. G.; Scaroni, A. W. Energy Fuels 2002, 16,
1463.
(c) Xu, X.; Song, C.; Miller, B. G.; Scaroni, A. W. Ind. Eng. Chem.
Res. 2005, 44, 8113.
(d) Xu, X.; Song, C.; Miller, B. G.; Scaroni, A. W.
Fuel Proc. Technol. 2005, 86, 1457.
5. Yue, M. B.; Chun, Y.; Cao, Y.; Dong, X.; Zhu, J. H. Adv. Funct. Mater.
2006, 16, 1717.
6. Kim, H. J.; Moon, J. H.; Park, J. W. J. Colloid Interface Sci. 2000, 227,
247.
7. (a) We are building on the work of Kim et al.6 who used flat silica materials for surface-initiated hyperbranching polymerization of aziridine to form aminosilica hybrid materials. Hicks, J. C.; Fauth, D.; Gray, M.; Jones, C. W. U.S. Patent Application 2006. (b) In parallel, Linden and coworkers8 reported similar materials but did not report an application.
8. Rosenholm, J. M.; Penninkangas, A.; Linden, M. Chem. Commun. 2006,
3909.
9. These experiments were systematically stopped after 200 min. If the experiments were allowed 250 min, capacities of 2.4 mmol CO2/g or 8.0 mmol CO2/g aziridine would be calculated.
10. (a) Hicks, J. C.; Dabestani, R.; Buchanan, A. C., III; Jones, C. W. Chem.
Mater. 2006, 18, 5022.
(b) Hicks, J. C.; Jones, C. W. Langmuir 2006, 22,
2676.
|
material |
analysis
temp ( |
mmol N /ga |
capacity/ capacity HA |
mmol CO2/ mmol N |
|
SBA-HA |
25 |
7.0 |
1.00 |
0.44 |
|
SBA-HA |
75 |
7.0 |
0.68 |
0.30 |
|
SBA/PEI(750 000 MW) |
25 |
7.4 |
0.64 |
0.27 |
|
SBA/PEI(750 000 MW) |
75 |
7.4 |
0.69 |
0.29 |
|
SBA/PEI(800 MW) |
25 |
10.9 |
ndb |
ndb |
|
SBA/PEI(800 MW) |
75 |
10.9 |
ndb |
ndb |
|
SBA-UNTEPA |
25 |
10.5 |
0.88 |
0.26 |
|
SBA-UNTEPA |
75 |
10.5 |
1.09 |
0.32 |
|
SBA-diamine |
25 |
2.5 |
0.23 |
0.28 |
|
SBA-NH2 |
25 |
1.9 |
0.13 |
0.21 |
a Values were determined from elemental analysis.b Capacities were not
determined or reproducable due to the tacky nature of the material from
the addition of PEI. The materials could not be dispersed in the packed-bed uniformly. All capacities are normalized to the capacity of SBA-HA at
25
C (3.11 mmol CO2/g sorbent).