Open-access Imidazolium-based Ionic Liquids Impregnated in Silica and Alumina Supports for CO2 Capture

Abstract

Ionic liquids (ILs) physical immobilization in solid materials is a key strategy for developing efficient and low cost CO2 capture processes. In this work, two porous commercial substrates with different characteristics (silica and alumina) were impregnated with ILs by physical wet method. Imidazolium based IL combined with [Br]- and [Tf2N]- anions were used in impregnation process. CO2 sorption capacity and selectivity (CO2/N2) of these materials were investigated. The best results regarding CO2/N2 selectivity and CO2 sorption were obtained with [Tf2N]- anion. In relation to solid support, commercial alumina exhibited enhanced CO2 uptake and higher selective capacity (CO2/N2) (6.1 (± 0.1)). Combination of commercial alumina as support and 20 wt% of mbmim [Tf2N] resulted in higher CO2/N2 selectivity of 9.5 ± 1.0. In addition, this material also showed fast sorption kinetics when compared to pure IL besides reuse capacity.

Keywords:
porous materials; ionic liquids; CO2 capture


1. Introduction

One of the main challenges is the increase in atmospheric CO2 concentration1. According to measurements, the mean CO2 level value is the highest already registered till date1,2. This fact underscores the need of reducing CO2 emissions from industrial sources (industrial processes and fossil fuels use/production) which are one of the main players contributing to this scenario2-5. Current processes for CO2 capture are associated with high cost, energy penalty and chemical production limiting its use. The most well-known process involves aqueous amine solutions6,7. Despite being widespread this process presents operational drawbacks (high energy for regeneration stage, degradation byproducts, equipment corrosion) that discourage its use5,8-13.

Ionic liquids (ILs) are a class of organic salts formed by combining organic cations and inorganic or organic anions resulting in compounds presenting melting temperature lower than 100°C14,15. ILs are candidates for replacing aqueous amine solution in CO2 capture processes15,16 due to their physico-chemical properties (like negligible vapor pressure) as well as CO2 sorption capacity1,17-20. Ionic liquids’ properties depend on cation and anion size, shape and nature21,22. Side chain branched imidazolium cation is considered promising for CO2 capture since it imparts sponge-like characteristics23. Moreover, anion nature has a great effect on gas solubility24. Fluorinated anions (such as [Tf2N]-) present high CO2 affinity25,26. In spite of this, ionic liquids present disadvantages as high viscosity limiting mass transfer27. In order to overcome limitations related to ILs high viscosity, as poor CO2 dynamics separation, ILs impregnation in solid materials appears as a good platform28. Solid materials such as silica and alumina hold large specific surface area, pore volume, tunable pore size and good stability being interesting candidates for applications in separation processes2,26,29-33. Besides these characteristics, some factors are fundamental to ensure these materials applicability, such as: fast kinetic, CO2 sorption capacity, CO2 selectivity, chemical and thermal stability1,34,35.

In this work we investigated anion and porous support effect on CO2 capture. Essential features to integrate this technique in large industrial systems such as CO2 sorption capacity, selectivity (CO2/N2), recyclability, sorption kinetics and thermal stability were evaluated. Commercial silica and alumina were used as solid supports impregnated with the ionic liquids mbmim [Br] and mbmim [Tf2N].

2. Experimental

2.1 Materials

1-Methylmidazole (99%, Sigma Aldrich), 1-Bromo-3-methylbutane (96%, Sigma Aldrich, Toluene (99.0%, Merck), Ether (Neon), Lithium trifluoromethanesulfonylimidate (Alfa Aesar, 98.0 %), Magnesium Sulfate (Merck), Dichloromethane (Anhydrol), Commercial Silica (S) and Commercial Alumina (A) were used as received.

2.2 Ionic Liquids synthesis

The ionic liquid mbmim[Br] (1- (3-methylbutyl) -3- methylimidazolium bromide) was synthesized as described by Andresova et al.36. Using this IL as starting material, anion exchange was carried out with lithium salt (LiTf2N) addition36, resulting in mbmim[Tf2N] (1- (3-methylbutyl) -3-methylimidazolium bis- (trifluoromethanesulfonylimide). ILs syntheses were confirmed by proton nuclear magnetic resonance (1H-NMR)36, in a Varian spectrophotometer, VNMRS 300 MHz, using DMSO-d6as solvent and 5 mm diameter glass tubes. mbmim[Br]:1H-RMN (300 MHz, DMSO-d6, 25°C), δ (ppm) 10.28 (m, 1H), 7.79 (t, 1H), 7.61 (t, 1H), 4.39-3.96 (m, 4H), 1.87-1.69 (m, 4H), 1.59 (m, 1H), 1.13 (m, 2H), 0.85 (t, 3H). mbmim[Tf2N]:1H-RMN (300 MHz, DMSO-d6, 25°C) δ (ppm) 9.13 (s, 1H), 7.79 (d, 1H), 7.70 (d, 1H), 4.24 (t, 2H), 3.85 (s,3H), 1.69 (m, 2H), 1.51 (m, 1H), 0.92 (d, 6H). ILs structures are depicted in Fig. 1.

Figure 1
ILs structure: a) mbmim[Br] b) mbmim[Tf2N].

2.3 Physical wet method immobilization

Ionic liquids immobilization in commercial porous substrates (silica S and alumina A) was performed by wet impregnation. In this technique the IL (mbmim[Br] or mbmim[Tf2N]) in concentrations of 10 to 30% wt is dissolved in dichloromethane; the contact with the support is effected manually with a pistil37. Samples were named as X-mbmim[Y]-Z, where X indicates the solid support (silica S or alumina A), Y the anion and Z the immobilized IL concentration. For example, S-mbmim[Tf2N]-10 means silica support, Tf2N anion and 10% wt of IL.

2.4 CO2 sorption and sorption kinetics assays

Pure and immobilized porous substrates sorption tests were performed statically through the cell-based pressure decay technique similar to that developed by Koros and Paul38. Tests were performed in triplicate at 45°C of temperature and 0.4 MPa (equilibrium pressure). CO2 solubility procedure, tests and calculation, was performed as presented in our previously published works2,39. Solid and liquid sorption kinetic was evaluated by controlling CO2 sorption until saturation amount over time. Recycle tests were performed by repeating sorption/desorption cycles five times at 0.4 MPa with desorption after each cycle by sample heating in an oven at 65 °C. Kinetic tests and solubility calculations for ionic liquids were performed just as in the case of solids, but with constant stirring of 800 rpm40.

2.5 CO2/N2 separation - Selectivity tests

Procedure for selectivity determination is well described in literature2,41. Tests were performed using a primary standard gaseous mixture with CO2 content of 15.89% and N2 balance. Experiments were carried out at equilibrium pressure of 2.3 MPa and temperature of 45°C. CO2 separation efficiency was calculated by equation 1, where Yi stands for molar fractions in the gas phase and Xi in the sorbed phase.

(1) S = XCO 2 YCO 2 XN 2 YN 2

2.6 Sample characterization

Materials structures were identified by FTIR. FTIR spectra were recorded on a PerkinElmer Spectrum100 spectrometer in UATR mode. Samples morphology was evaluated by Field Emission Scanning Electron Microscopy (FESEM) and performed on a FEI Inspect F50 equipment in secondary electron mode. Samples thermal stability and immobilized IL content were evaluated by TGA/DTG (TA Instruments SDT-Q600), under nitrogen inert atmosphere from 25 to 800ºC and heating rate of 20ºC/min. Samples porous nature was investigated by N2 adsorption/desorption technique and the specific surface area was calculated using the Brunauer - Emmett - Teller (BET) method. Nitrogen adsorption-desorption isotherm was obtained using NOVA 4200 High Speed ​​at liquid nitrogen temperature. Bulk density was obtained by measuring in a vessel, dispersed powder volume and weight, under gravity influence. Skeleton density was determined by helium pycnometry (Ultrafoam ™ 1200e, Quantachrome Instruments). Porosity (%) was theoretically calculated using density and skeletal density results according to literature procedure42. IL samples content was determined by TGA in the range of 150 to 800°C using equation 2. The weight loss of sample S (3.4%) and sample A (17.6%) without IL loading was used as control and subtracted from obtained value from equation 2. For silica the observed weight loss up to 150°C corresponds to water loss. On the other hand, for alumina, besides weight loss related to moisture, there is also a weight loss corresponding to bohemite percentage and crystallites size43.

(2) IL % = W 150 W 800 W 150 X 100

Where W150 and W800 are weight (g) at 150°C and 800°C, respectively.

3. Results and Discussion

FTIR spectra of solid supports (S and A) as well as solid supports impregnated with ILs are shown in Fig. 2. Immobilized samples with different IL content presented similar behavior, so samples with 30% of ILs mbmim[Br] and mbmim[Tf2N] are used to illustrate the immobilization in silica support (S) and mbmim[Tf2N] to illustrate IL immobilization in alumina sample (A). In sample S (Fig. 2a) spectrum characteristic silica bands are observed2,44: at 3352 cm-1, 1635 cm-1 (hydroxyl), 1066 cm-1 (condensed silica Si-O-Si) and from 968 cm-1 to 798 cm-1 (Si-OH). With ILs immobilization (Fig. 2a) one can observe the appearance of imidazolium cation characteristic bands at45: 2973 cm-1 (C-H of CH2), 1633-1625 cm-1 (C=N aromatic), 1571-1471 cm-1 (C=C aromatic), 1349 cm-1 (C-N aromatic), 1192 cm-1 (C-N aliphatic) and for [Tf2N] anion at45: 1054 cm-1 (N-S), 792 cm-1 (C-S), 741-657 cm-1 (C-F); and [Br]46: 655 cm-1 (C-Br). Sample A FTIR spectrum (Fig. 2b) evidenced characteristics bands at47,48: 660 cm-1 (aluminum in oxide octahedral coordination), from 890 to 734 cm-1 (tetracoordinated aluminum). The band at 1060 cm-1 corresponds to Al-OH48. The bands at 1639 cm-1 and 3200 cm-1 correspond to angular and axial deformation of hydroxyls group, respectively47,48. The band at 1395 cm-1 is attributed to nitrate (NO3-) and at 3089 cm-1 to alkyl groups (-CH2/-CH3) probably from fabrication process47,48. With IL mbmim[Tf2N] immobilized in sample A (Fig. 2b) one can observe the appearance of imidazolium characteristic bands at45: 2966 cm-1 (C-H of CH2), 2878 cm-1 (C-H of CH3), 1571-1469 cm-1 (C=C aromatic), 1348 cm-1 (C-N aromatic), 1186-1135 cm-1 (C-N aliphatic) and for [Tf2N] anion at45: 1056 cm-1 (N-S), 876 cm-1 (N-S), 731 cm-1 (C-F).

Figure 2
FTIR for samples: a) S, S-mbmim[Br]-30, S-mbmim[Tf2N]-30; b) A and and A- mbmim[Tf2N]-30.

Fig. 3 presents FESEM images for samples S and A as well as samples S-mbmim[Tf2N]-30 and A-mbmim[Tf2N]-30. Comparing sample S micrograph (Fig. 3, a) with sample S-mbmim[Tf2N]-30 (Fig. 3, b) one can observe an increase in particle size with IL immobilization (from ~25 µm to ~120 µm). For sample A-mbmim[Tf2N]-30 (Fig. 3, d) an increase in particle size also was observed (from ~24 µm to ~36 µm) when compared to sample A (Fig. 3, c). Particle size increases under IL immobilization. This behavior is probably related to particle agglomeration for both samples.

Figure 3
FESEM for samples: (a) S; (b) S-mbmim[Tf2N]-30; (c) A; (d) A-mbmim[Tf2N]-30.

Table 1 shows the amount of immobilized IL in supports S and A determined by TGA. The actual percentage values obtained for both supports (S and A) were close to the theoretical one evidencing process efficiency.

Table 1
Amount (%) of immobilized IL in supports S and A determined by TGA.

N2 adsorption/desorption isotherm tests at 77K were performed for all samples (Figure 4). Typical type IV curves with H3 hysteresis loop according to IUPAC classification were observed in all cases (Figure 4A)49-51 except for sample A-mbmim[Tf2N]-30 (Figure 4B). Sample A-mbim[Tf2N]-30 presented a isotherm characteristic of non-porous materials (type III). This behavior is possibly due to the amount of immobilized IL (30%) resulting in pore saturation altering its textural properties51-53 (see Table 2).

Figure 4
N2 isotherms of adsorption (○) and desorption (□): (A) A-mbmim[Tf2N]-20; (B) A-mbmim[Tf2N]-30.

Table 2
Density and pore characteristics of all samples (S and A with and without IL immobilization).

Table 2 summarizes density and textural properties of all samples studied in this work. It is possible to observe that regardless the anion or the support, porosity, specific surface area, pore volume and pores radius were reduced with ILs immobilization. We can also highlight that the higher the ILs content the lower these values were probably due to pore filling. These data corroborates several studies reporting textural properties decrease after organic loading2,49-51 and also confirm that the relationship between bulk density and porosity is inversely proportional54.

3.1 Influence of anion on CO2 sorption capacity

Fig. 5 presents sorption values at 45°C of temperature and 0.4 MPa of pressure for sample S and the ILs mbmim[Br]- and mbmim[Tf2N]-, with different IL content, immobilized on sample S. It can be seen that sample S presents the highest CO2 sorption capacity (81.7 (± 2.2) mg CO2/g) when compared to immobilized samples. This behavior is possibly associated with its high specific surface area (487 m2/g). Polar groups (Si-OH) on sample S surface also can improve CO2 sorption due to affinity with CO255. Regarding immobilized ILs a tendency in CO2 sorption capacity reduction with IL content increase was observed for both anions (S-mbmim[Br]-10 71.7 (± 2.6) mg CO2/g; S-mbmim[Br]-20 54.8 (± 1.0) mg CO2/g; S-mbmim[Br]-30 55.1 (± 1.3) mg CO2/g ; S-mbmim[Tf2N]-10 56.0 (± 0.7) mg CO2/g; S-mbmim[Tf2N]-20 55.8 (± 1.0) mg CO2/g); S-mbmim[Tf2N]-30 45.2 (± 2.3) mg CO2/g). This behavior is probably related to specific surface area and porosity reduction with IL immobilization (see Table 2). From results, one can infer that IL content and anion type has a secondary influence on sorption values. On the other hand, specific surface area is the main factor influencing CO2 sorption capacity. Higher sorption capacity was observed for sample S-mbmim [Br]-10 (71.7 (± 2.6) mg CO2/g; S= 441 m2/g) when compared to other samples containing IL with less important specific surface area values. Similar behavior was described by Kim et al.56. Results obtained in this work for silica samples/immobilized ILs were similar or higher than those reported in literature under the same pressure and temperature conditions (~55 mg CO2/g) for 10% amine (PEI and PEHA) immobilized on mesoporous silica57.

Figure 5
CO2 sorption capacity at 0.4 MPa and 45°C.

CO2/N2 selectivity for sample S as well as for sample S immobilized with ILs is depicted in Fig. 6. As seen, ILs immobilization improves silica samples selectivity. This behavior is probably related to imidazolium ring polarity58,59 and IL content60. Yet, ionic liquids have more affinity for CO2 when compared to other gases such as CH4 and N261. The best result regarding selectivity was observed for anion [Tf2N] and sample S-mbmim[Tf2N]-30 of (7.9 (± 0.2)). This result is in accordance with literature which describes [Tf2N] having high CO2 selectivity in gas mixtures when compared to other anions57. The best sorption capacity was obtained for sample S, but the higher separation efficiency (CO2/N2) was obtained by mbmim[Tf2N]-30 sample. This parameter has a direct impact on product purity degree, playing an important role in sorbent choice35. The presence of [Tf2N] anion results in the best material for CO2 capture. In the next section support performance evaluation will be described using mbmim[Tf2N] as IL.

Figure 6
Selectivity at 2.3 MPa of pressure and 45°C of temperature.

3.2 Solid support role in CO2 sorption capacity and CO2/N2 selectivity

Table 3 presents the results obtained for CO2 sorption and CO2/N2 selectivity for sample A and sample A immobilized with the IL mbmim[TF2N] in different content in comparison with sample S and sample S with the IL mbmim[TF2N] in different content as well.

Table 3
CO2 sorption capacity and CO2/N2 selectivity for samples S and A with and without IL immobilization.

Analyzing the supports sorption capacity one can notice that sample A has lower sorption capacity (61.1 (± 1.2) mg CO2/g) once compared to sample S (81.7 (± 2.2)). This behavior is related to sample S specific surface area being twice as large as sample A (Table 2). Unlike CO2 sorption, selectivity (CO2/N2) of sample A is higher when compared to sample S. This behavior is attributed to metal presence in sample A improving support/CO2 affinity1,58,59,62,63. Comparing CO2 sorption capacity of IL immobilized samples one can observe a reduction in CO2 sorption values for all samples. This behavior is related to the decrease in textural properties (see Table 2), except for sample A-mbmim[Tf2N]-30 which CO2 sorption capacity is similar to sample A. CO2 sorption capacity of sample A-mbmim[Tf2N]-30 may be related to the type III isotherm (Fig. 4) presented by this sample64. Chen et al.52 also observed similar behavior to that obtained for sample A-mbmim[Tf2N]-30 when immobilizing PEI (polyethylenimine) in mesoporous alumina. IL immobilization increased CO2 efficiency removal in relation to N2, when compared to pure supports. This behavior is attributed to higher IL/CO2 affinity than support/CO22,65. Selectivity is directly influenced by immobilized IL content. For support S, increasing IL content continuously increased selectivity. For sample A this tendency was observed until IL content of 20%. For 30% a selectivity reduction was observed probably due to the non-porous behavior (Fig. 4) and also to the fact that the IL reduces CO2/support metal interaction. Sample A-mbmim[Tf2N]-20 was more selective and choosen to perform kinetic and recycle tests.

3.3 Kinetics tests

Fig. 7 presents kinetic behavior of immobilized sample A-mbmim[Tf2N]-20 compared to kinetic behavior of pure IL mbmim[Tf2N]. It is interesting to note that immobilized ionic liquid presents CO2 sorption (42.7 (± 2.3) mg CO2/g) capacity higher than pure IL (14.6 (± 0.5) mg CO2/g). In addition, kinetics improves dramatically with immobilization. Pure IL is extremely viscous, needing longer times for CO2 uptake (350 min). In contrast, IL immobilization in solid supports improves mass transfer, resulting in a faster CO2 sorption process (10 min)27,66-68.

Figure 7
Time course of CO2 uptake in neat: (▲) mbmim[Tf2N]; (●) A-mbmim[Tf2N]-20.

3.4 Recycle tests

Fig. 8 shows sorption/desorption tests aiming sample A-mbmim[Tf2N]-20 stability evaluation. After 5 sorption/desorption cycles, CO2 sorption in A-mbmim[Tf2N]-20 was reversible confirming sample stability and reuse.

Figure 8
Recycle test: five sorption/desorption cycles applied to the sample A-mbmim[Tf2N]-20.

4. Conclusions

Imidazolium based IL with different anions were immobilized by wet point method in two different supports. CO2 sorption capacity and CO2/N2 selectivity were evaluated. When analyzing anion influence we observed that anion [Tf2N]- presented superior performance in relation to CO2 selectivity when compared to [Br]- anion, possibly due to the higher CO2 affinity of fluorinated anions. When comparing supports (alumina and silica), commercial alumina seems to be a good material for this purpose since it combined textural properties (specific surface area, volume and pore radius) with selectivity due to metal presence on its surface. This combination favored its performance in CO2/N2 selectivity when the concentration of immobilized IL was 20%. The best combination of support and ionic liquid content was obtained with sample A-mbmim[Tf2N]-20.

5. Acknowledgment

Authors would like to thank PETROBRAS for its financial support. Sandra Einloft thanks CNPq for research grant. This study was financed in part by the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior - Brasil (CAPES) - Finance Code 001.

6. References

  • 1 Mohamedali M, Nath D, Ibrahim H, Henni A. Review of Recent Developments in CO2 Capture Using Solid Materials: Metal Organic Frameworks (MOFs). In: Moya BL, Pous J, editors. Greenhouse Gases London: IntechOpen; 2016. p. 115-154. Available from: http://www.intechopen.com/books/greenhouse-gases/review-of-recent-developments-in-co2-capture-using-solid-materials-metal-organic-frameworks-mofs-
    » http://www.intechopen.com/books/greenhouse-gases/review-of-recent-developments-in-co2-capture-using-solid-materials-metal-organic-frameworks-mofs-
  • 2 Duczinski R, Bernard F, Rojas M, Duarte E, Chaban V, Vecchia FD, et al. Waste derived MCMRH- supported IL for CO2/CH4 separation. Journal of Natural Gas Science and Engineering 2018;54:54-64. Available from: http://linkinghub.elsevier.com/retrieve/pii/S1875510018301446
    » http://linkinghub.elsevier.com/retrieve/pii/S1875510018301446
  • 3 Yuan Z, Eden MR. Toward the Development and Deployment of Large-Scale Carbon Dioxide Capture and Conversion Processes. Industrial and Engineering Chemistry Research 2016;55(12):3383-419.
  • 4 Kadam R, Panwar NL. Recent advancement in biogas enrichment and its applications. Renewable and Sustainable Energy Reviews 2017;73:892-903. Available from: http://dx.doi.org/10.1016/j.rser.2017.01.167
    » http://dx.doi.org/10.1016/j.rser.2017.01.167
  • 5 Wang Y, Zhao L, Otto A, Robinius M, Stolten D. A Review of Post-combustion CO2 Capture Technologies from Coal-fired Power Plants. Energy Procedia 2017;114:650-65. Available from: http://dx.doi.org/10.1016/j.egypro.2017.03.1209
    » http://dx.doi.org/10.1016/j.egypro.2017.03.1209
  • 6 Koytsoumpa EI, Bergins C, Kakaras E. The CO2 economy: Review of CO2 capture and reuse technologies. Journal of Supercritical Fluids 2018;132:3-16.
  • 7 Guido G, Compagnoni M, Pellegrini LA, Rossetti I. Mature versus emerging technologies for CO2 capture in power plants: Key open issues in post-combustion amine scrubbing and in chemical looping combustion. Frontiers of Chemical Science and Engineering 2018;12(2):315-25.
  • 8 Leung DYC, Caramanna G, Maroto-Valer MM. An overview of current status of carbon dioxide capture and storage technologies. Renewable and Sustainable Energy Reviews 2014;39:426-43. Available from: http://dx.doi.org/10.1016/j.rser.2014.07.093
    » http://dx.doi.org/10.1016/j.rser.2014.07.093
  • 9 Kang G, Chan ZP, Saleh SBM, Cao Y. Removal of high concentration CO2 from natural gas using high pressure membrane contactors. International Journal of Greenhouse Gas Control 2017;60:1-9. Available from: http://dx.doi.org/10.1016/j.ijggc.2017.03.003
    » http://dx.doi.org/10.1016/j.ijggc.2017.03.003
  • 10 Song C, Liu Q, Ji N, Deng S, Zhao J, Kitamura Y. Natural gas purification by heat pump assisted MEA absorption process. Applied Energy 2017;204:353-61.
  • 11 Kothandaraman A, Nord L, Bolland O, Herzog HJ, McRae GJ. Comparison of solvents for post-combustion capture of CO2 by chemical absorption. Energy Procedia 2009;1(1):1373-80. Available from: http://dx.doi.org/10.1016/j.egypro.2009.01.180
    » http://dx.doi.org/10.1016/j.egypro.2009.01.180
  • 12 Thouchprasitchai N, Pintuyothin N, Pongstabodee S. Optimization of CO2 adsorption capacity and cyclical adsorption / desorption on tetraethylenepentamine-supported surface-modified hydrotalcite. Journal of Environmental Sciences 2017;65:293-305. Available from: http://dx.doi.org/10.1016/j.jes.2017.02.015
    » http://dx.doi.org/10.1016/j.jes.2017.02.015
  • 13 Ünveren EE, Monkul BÖ, Sarıoğlan Ş, Karademir N, Alper E. Solid amine sorbents for CO2 capture by chemical adsorption: A review. Petroleum 2016;3(1):37-50.
  • 14 Wilkes JS. A Short History of Ionic Liquids - From Molten Salts to Neoteric Solvents. Green Chem 2002;4(2):73-80.
  • 15 Figueroa JD, Fout T, Plasynski S, McIlvried H, Srivastava RD. Advances in CO2 capture technology-The U.S. Department of Energy’s Carbon Sequestration Program. International Journal of Greenhouse Gas Control 2008;2(1):9-20.
  • 16 Anthony JL, Anderson JL, Maginn EJ, Brennecke JF. Anion Effects on Gas Solubility in Ionic Liquids. The Journal of Physical Chemistry B 2005;109(13):6366-74.
  • 17 Lei Z, Dai C, Chen B. Gas solubility in ionic liquids. Chemical Reviews 2014;114(2):1289-326. Available from: http://www.ncbi.nlm.nih.gov/pubmed/24195614
    » http://www.ncbi.nlm.nih.gov/pubmed/24195614
  • 18 Ramdin M, Amplianitis A, Bazhenov S, Volkov A, Volkov V, Vlugt TJH, et al. Solubility of CO2 and CH4 in ionic liquids: Ideal CO2/CH4 selectivity. Industrial and Engineering Chemistry Research 2014;53(40):15427-35.
  • 19 Brennecke JF, Gurkan BE. Ionic liquids for CO2 capture and emission reduction. Journal of Physical Chemistry Letters 2010;1(24):3459-64.
  • 20 Paolone A, Palumbo O, Trequattrini F, Appetecchi GB. Relaxational Dynamics in the PYR14-IM14 Ionic Liquid by Mechanical Spectroscopy. Materials Research 2018; 21. Available from: http://dx.doi.org/10.1590/1980-5373-MR-2017-0870
    » http://dx.doi.org/10.1590/1980-5373-MR-2017-0870
  • 21 Sarmad S, Mikkola JP, Ji X. Carbon Dioxide Capture with Ionic Liquids and Deep Eutectic Solvents: A New Generation of Sorbents. ChemSusChem 2017;10(2):324-52.
  • 22 Karimi B, Tavakolian M, Akbari M, Mansouri F. Ionic Liquids in Asymmetric Synthesis: An Overall View from Reaction Media to Supported Ionic Liquid Catalysis. ChemCatChem 2018;10(15):3173-205.
  • 23 Corvo MC, Sardinha J, Casimiro T, Marin G, Seferin M, Einloft S, et al. A rational approach to CO2 capture by imidazolium ionic liquids: Tuning CO2 solubility by cation alkyl branching. ChemSusChem 2015;8(11):1935-46.
  • 24 Anthony JL, Anderson JL, Maginn EJ, Brennecke JF. Anion Effects on Gas Solubility in Ionic Liquids. Journal of Physical Chemistry B 2005;109(13):6366-74. Available from: http://pubs.acs.org/doi/abs/10.1021/jp046404l
    » http://pubs.acs.org/doi/abs/10.1021/jp046404l
  • 25 Aki SNVK, Mellein BR, Saurer EM, Brennecke JF. High-pressure phase behavior of carbon dioxide with imidazolium-based ionic liquids. Journal of Physical Chemistry B 2004;108(52):20355-20365.
  • 26 Aquino AS, Bernard FL, Borges JV, Mafra L, Vecchia FD, Vieira MO, et al. Rationalizing the role of the anion in CO2 capture and conversion using imidazolium-based ionic liquid modified mesoporous silica. RSC Advances Royal Society of Chemistry 2015;5(79):64220-7.
  • 27 Safiah MN, Azmi BM, Normawati MY. CO2 Capture Using Silica and Molecular Sieve Impregnated with [hmim][Tf2N]. International Journal of Chemical Engineering and Applications 2014;5(4):342-6. Available from: http://www.ijcea.org/index.php?m=content&c=index&a=show&catid=57&id=740
    » http://www.ijcea.org/index.php?m=content&c=index&a=show&catid=57&id=740
  • 28 Lemus J, Silva FA, Palomar J, Carvalho PJ, Coutinho JAP. Solubility of carbon dioxide in encapsulated ionic liquids. Separation and Purification Technology 2018;196:41-6. Available from: https://doi.org/10.1016/j.seppur.2017.08.032
    » https://doi.org/10.1016/j.seppur.2017.08.032
  • 29 Guillet-Nicolas R, Bérubé F, Thommes M, Janicke MT, Kleitz F. Selectively tuned pore condensation and hysteresis behavior in mesoporous SBA-15 silica: Correlating material synthesis to advanced gas adsorption analysis. Journal of Physical Chemistry: C 2017;121(44):24505-26.
  • 30 Lashaki MJ, Ziaei-Azad H, Sayari A. Insights into the Hydrothermal Stability of Triamine-Functionalized SBA-15 Silica for CO2 Adsorption. ChemSusChem 2017;10(20):4037-45.
  • 31 Xu X, Song C, Andresen JM, Miller BG, Scaroni AW. Preparation and characterization of novel CO2 “molecular basket” adsorbents based on polymer-modified mesoporous molecular sieve MCM-41. Microporous Mesoporous Materials 2003;62(1-2):29-45.
  • 32 Sánchez Fuentes CE, Guzmán-Lucero D, Torres-Rodriguez M, Likhanova NV, Bolaños JN, Olivares-Xometl O, et al. CO2/N2 separation using alumina supported membranes based on new functionalized ionic liquids. Separation and Purification Technology 2017;182:59-68.
  • 33 Magalhaes GC, Ribeiro JON, Vasconcelos DCL, Vasconcelos WL. Production of Pure Granules of Sba-15 Mesoporous Silica. Materials Research 2018;21(6):e20180148.
  • 34 Nanda S, Reddy SN, Mitra SK, Kozinski JA. The progressive routes for carbon capture and sequestration. Energy Science Engineering 2016;4(2):99-122.
  • 35 Ben-Mansour R, Habib MA, Bamidele OE, Basha M, Qasem NAA, Peedikakkal A, et al. Carbon capture by physical adsorption: Materials, experimental investigations and numerical modeling and simulations - A review. Applied Energy 2016;161:225-55. Available from: http://dx.doi.org/10.1016/j.apenergy.2015.10.011
    » http://dx.doi.org/10.1016/j.apenergy.2015.10.011
  • 36 Andresova A, Storch J, Traïkia M, Wagner Z, Bendova M, Husson P. Branched and cyclic alkyl groups in imidazolium-based ionic liquids: Molecular organization and physico-chemical properties. Fluid Phase Equilibria 2014;371:41-9. Available from: http://dx.doi.org/10.1016/j.fluid.2014.03.004
    » http://dx.doi.org/10.1016/j.fluid.2014.03.004
  • 37 Haber J, Block JH, Delmon B. Manual of methods and procedures for catalyst characterization (Technical Report). Pure and Applied Chemistry 1995;67(8-9):1257-306. Available from: https://www.degruyter.com/view/j/pac.1995.67.issue-8-9/pac199567081257/pac199567081257.xml
    » https://www.degruyter.com/view/j/pac.1995.67.issue-8-9/pac199567081257/pac199567081257.xml
  • 38 Koros WJ, Paul DR. Design considerations for measurement of gas sorption in polymers by pressure decay. Journal of Polymer Science: Polymer Physics Edition 1976;14(10):1903-7. Available from: http://doi.wiley.com/10.1002/pol.1976.180141014
    » http://doi.wiley.com/10.1002/pol.1976.180141014
  • 39 Bernard FL, Polesso BB, Cobalchini FW, Chaban VV, Nascimento JF, Vecchia FD, et al. Hybrid Alkoxysilane-Functionalized Urethane-Imide-Based Poly(ionic liquids) as a New Platform for Carbon Dioxide Capture. Energy and Fuels 2017;31(9):9840-9.
  • 40 Jacquemin J, Gomes MFC, Husson P, Majer V. Solubility of carbon dioxide, ethane, methane, oxygen, nitrogen, hydrogen, argon, and carbon monoxide in 1-butyl-3-methylimidazolium tetrafluoroborate between temperatures 283 K and 343 K and at pressures close to atmospheric. Journal of Chemical Thermodynamics 2006;38(4):490-502.
  • 41 Azimi A, Mirzaei M. Experimental evaluation and thermodynamic modeling of hydrate selectivity in separation of CO2 and CH4 Chemical Engineering Research and Design 2016;111:262-8. Available from: http://dx.doi.org/10.1016/j.cherd.2016.05.005
    » http://dx.doi.org/10.1016/j.cherd.2016.05.005
  • 42 Tokudome Y, Nakanishi K, Kanamori K, Fujita K, Akamatsu H, Hanada T. Structural characterization of hierarchically porous alumina aerogel and xerogel monoliths. Journal of Colloid and Interface Science 2009;338(2):506-13.
  • 43 Tettenhorst TR, Hofmann DA. Crystal Chemistry of Boehmite. Clays and Clay Minerals 1980;28(5):373-80.
  • 44 Bakar RA, Yahya R, Gan SN. Production of High Purity Amorphous Silica from Rice Husk. Procedia Chemistry 2016;19:189-95. Available from: http://linkinghub.elsevier.com/retrieve/pii/S1876619616001388
    » http://linkinghub.elsevier.com/retrieve/pii/S1876619616001388
  • 45 Zhang X, Guo W, Wu Y, Gong L, Li W, Li X, et al. Cationic polymerization of p-methylstyrene in selected ionic liquids and polymerization mechanism. Polymer Chemistry 2016;7(32):5099-5112. Available from: http://dx.doi.org/10.1039/c6py00796a
    » http://dx.doi.org/10.1039/c6py00796a
  • 46 Cha S, Ao M, Sung W, Moon B, Ahlström B, Johansson P, et al. Structures of ionic liquid-water mixtures investigated by IR and NMR spectroscopy. Physical Chemistry Chemical Physics 2014;16(20):9591-601.
  • 47 Trombetta M, Busca G, Willey RJ. Characterization of silica-containing aluminum hydroxide and oxide aerogels. Journal of Colloid and Interface Science 1997;190(2):416-26.
  • 48 Musić S, Dragčević D, Popović S. Hydrothermal crystallization of boehmite from freshly precipitated aluminum hydroxide. Materials Letters 1999;40(6):269-74.
  • 49 Balsamo M, Erto A, Lancia A, Totarella G, Montagnaro F, Turco R. Post-combustion CO2 capture: On the potentiality of amino acid ionic liquid as modifying agent of mesoporous solids. Fuel 2018;218:155-61. Available from: https://doi.org/10.1016/j.fuel.2018.01.038
    » https://doi.org/10.1016/j.fuel.2018.01.038
  • 50 Ji X, Tang S, Gu L, Liu T, Zhang X. Synthesis of rod-like mesoporous γ-Al2O3 by an ionic liquid-assisted sol-gel method. Materials Letters 2015;151:20-3. Available from: http://dx.doi.org/10.1016/j.matlet.2015.03.022
    » http://dx.doi.org/10.1016/j.matlet.2015.03.022
  • 51 Thommes M, Kaneko K, Neimark AV, Olivier JP, Rodriguez-Reinoso F, Rouquerol J, et al. Physisorption of gases, with special reference to the evaluation of surface area and pore size distribution (IUPAC Technical Report). Pure and Applied Chemistry 2015;87(9):1051-69.
  • 52 Chen C, Ahn WS. CO2 capture using mesoporous alumina prepared by a sol-gel process. Chemical Engineering Journal 2011;166(2):646-51. Available from: http://dx.doi.org/10.1016/j.cej.2010.11.038
    » http://dx.doi.org/10.1016/j.cej.2010.11.038
  • 53 Žilková N, Zukal A, Čejka J. Synthesis of organized mesoporous alumina templated with ionic liquids. Microporous and Mesoporous Materials 2006;95(1-3):176-9.
  • 54 Kakaire J, Makokha GL, Mwanjalolo M, Mensah AK, Emmanuel M. Effects of Mulching on Soil Hydro-Physical Properties in Kibaale Sub-catchment, South Central Uganda. Applied Ecology and Environmental Sciences 2015;3(5):127-135..
  • 55 Rimola A, Costa D, Sodupe M, Lambert JF, Ugliengo P. Silica surface features and their role in the adsorption of biomolecules: Computational modeling and experiments. Chemical Reviews 2013;113(6):4216-313.
  • 56 Kim HJ, Yang HC, Chung DY, Yang IH, Choi YJ, Moon JK. Functionalized Mesoporous Silica Membranes for CO2 Separation Applications. Journal of Chemistry 2015;1-9.
  • 57 Sanz R, Calleja G, Arencibia A, Sanz-Pérez ES. CO2 capture with pore-expanded MCM-41 silica modified with amino groups by double functionalization. Microporous and Mesoporous Materials 2015;209:165-71.
  • 58 Hojniak SD, Silverwood IP, Khan AL, Vankelecom IFJ, Dehaen W, Kazarian SG, et al. Highly selective separation of carbon dioxide from nitrogen and methane by nitrile/glycol-difunctionalized ionic liquids in supported ionic liquid membranes (SILMs). Journal of Physical Chemistry: B 2014;118(26):7440-9.
  • 59 Salehi S, Anbia M. High CO2 Adsorption Capacity and CO2/CH 4 Selectivity by Nanocomposites of MOF-199. Energy & Fuels 2017;31(5):5376-84. Available from: http://pubs.acs.org/doi/abs/10.1021/acs.energyfuels.6b03347
    » http://pubs.acs.org/doi/abs/10.1021/acs.energyfuels.6b03347
  • 60 Zhu J, He B, Huang J, Li C, Ren T. Effect of immobilization methods and the pore structure on CO2 separation performance in silica-supported ionic liquids. Microporous and Mesoporous Materials 2018;260:190-200. Available from: https://doi.org/10.1016/j.micromeso.2017.10.035
    » https://doi.org/10.1016/j.micromeso.2017.10.035
  • 61 Anthony JL, Maginn EJ, Brennecke JF. Solubilities and thermodynamic properties of gases in the ionic liquid 1-n-butyl-3-methylimidazolium hexafluorophosphate. Journal of Physical Chemistry: B 2002;106(29):7315-20.
  • 62 Cabello CP, Rumori P, Palomino GT. Carbon dioxide adsorption on MIL-100(M) (M = Cr, V, Sc) metal-organic frameworks: IR spectroscopic and thermodynamic studies. Microporous and Mesoporous Materials 2014;190:234-9. Available from: http://dx.doi.org/10.1016/j.micromeso.2014.02.015
    » http://dx.doi.org/10.1016/j.micromeso.2014.02.015
  • 63 Campbell S, Bernard FL, Rodrigues DM, Rojas MF, Carreño LA, Chaban VV, et al. Performance of metal-functionalized rice husk cellulose for CO2 sorption and CO2/N2 separation. Fuel 2019;239:737-46.
  • 64 Sing KSW, Everett DH, Haul RAW, Moscou L, Pierotti RA, Rouquérol J, et al. Reporting Physisorption Data For Gas / Solid Systems with Special Reference to the Determination of S. Pure and Applied Chemistry 1985;57(4):603-19.
  • 65 Arellano IH, Madani SH, Huang J, Pendleton P. Carbon dioxide adsorption by zinc-functionalized ionic liquid impregnated into bio-templated mesoporous silica beads. Chemical Engineering Journal 2016;283:692-702. Available from: http://dx.doi.org/10.1016/j.cej.2015.08.006
    » http://dx.doi.org/10.1016/j.cej.2015.08.006
  • 66 Aboudi J, Vafaeezadeh M. Efficient and reversible CO2 capture by amine functionalized-silica gel confined task-specific ionic liquid system. Journal of Advanced Research 2015;6(4):571-7. Available from: http://dx.doi.org/10.1016/j.jare.2014.02.001
    » http://dx.doi.org/10.1016/j.jare.2014.02.001
  • 67 Vilarrasa-Garcia E, Moya EMO, Cecilia JA, Cavalcante Junior CL, Jiménez-Jiménez J, Azevedo DCS, et al. CO2 adsorption on amine modified mesoporous silicas: Effect of the progressive disorder of the honeycomb arrangement. Microporous and Mesoporous Materials 2015;209:172-83. Available from: http://dx.doi.org/10.1016/j.micromeso.2014.08.032
    » http://dx.doi.org/10.1016/j.micromeso.2014.08.032
  • 68 Yang N, Wang R. Molecular sieve supported ionic liquids as efficient adsorbent for CO2 capture. Journal of the Serbian Chemical Society 2015;80(2):265-75.

Publication Dates

  • Publication in this collection
    11 Nov 2019
  • Date of issue
    2019

History

  • Received
    06 Dec 2018
  • Reviewed
    26 June 2019
  • Accepted
    17 July 2019
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