Sara Sorribasa,
Bibiana Comesaña-Gándarab,
Angel E. Lozanobc,
Beatriz Zornozaa,
Carlos Télleza and
Joaquín Coronas*a
aChemical and Environmental Engineering Department and Instituto de Nanociencia de Aragón (INA), Universidad de Zaragoza, 50018 Zaragoza, Spain. E-mail: coronas@unizar.es; Fax: +34 976 761879; Tel: +34 976 762471
bDepartment of Macromolecular Chemistry, Institute of Polymer Science and Technology, ICTP-CSIC, 28006 Madrid, Spain
cSMAP, UVA-CSIC Research Unit, University of Valladolid, 47011 Valladolid, Spain
First published on 23rd November 2015
An in-depth study into the synthesis of the titanosilicate ETS-10 has been carried out to obtain crystals with different particle sizes, roughness and porosity. The effect of these parameters on the CO2/CH4 gas separation performance using mixed matrix membranes (MMMs) has been studied. MMMs based on ETS-10 polycrystalline particles of 1–2 μm in size with high surface roughness and porosity gave rise to a good filler dispersion and filler–polymer interaction. The addition of 10 wt% ETS-10 polycrystalline particles into the polysulfone matrix increased the CO2 permeability from 6.1 to 7.8 Barrer and the CO2/CH4 selectivity from 31 to 38. When using the polyimide 6FDA-6FpDA, a glassy polymer with high gas permeability, the addition of 10 wt% ETS-10 polycrystalline particles increased the CO2 permeability from 96 to 125 Barrer, with a decrease in CO2/CH4 selectivity from 56 to 51.
MMMs are an excellent strategy to overcome the trade-off between permeability and selectivity for polymeric membranes. The use of two materials with different gas separation behaviors offers the possibility of designing an efficient membrane combining the advantages of both phases: the easy processability and low cost of the polymer with the superior gas separation performance of the nanostructured fillers.11–13 Also, the incorporation of these specific materials within the polymeric matrix generally provides enhanced physical, mechanical and thermal properties for their use in aggressive environments and a membrane stabilization system against changes in permeability with the temperature.14
ETS-10 inorganic membranes on α-alumina supports have previously been used in the separation of propylene/propane mixtures,15,16 and in the separation of CO2 mixtures (CO2/N2, CO2/H2),17 since ETS-10 is a basic nature material which can adsorb CO2 at low temperatures.18 Regarding MMMs based on the titanosilicate ETS-10, Burmann et al.19 prepared 8 wt% ETS-10-polysulfone MMMs via spin coating for H2/CH4 and O2/N2 gas separation mixtures, obtaining a slight improvement in gas permeability/selectivity compared to the bare polymer film. Chitosan (CS) and microporous titanosilicate ETS-10/CS MMMs were prepared and tested for pervaporation of water/ethanol mixture increasing flux with respect to the pure CS membranes.20
Polysulfone (PSF), whose structure is shown in Fig. 1a, is an important commercial membrane material for gas separation due to its excellent mechanical properties, wide operating temperature range, fairly good chemical resistance, easy fabrication and low price.21 However, its great rigidity due to its high degree of molecular immobility leads to low permeabilities. To improve the permeability and selectivity of gas separation polymeric membranes, the incorporation of bulky groups in the chains of glassy polymers makes their structure stiffer and hinders an efficient packing of the chains, leading to an increase in free volume. The high volume fractions with restrictive or selective channels increase the diffusivity of gases, and thus their permeability. An example of such a kind of polymer is the fluorinated polyimide 6FDA-6FpDA, whose structure is shown in Fig. 1b. Fluorinated polyimides are particularly interesting for gas separation because they have good mechanical, thermal and transport properties.22 6FDA-6FpDA is an aromatic polyimide having two hexafluoropropane moieties. This polyimide is soluble in many common organic solvents including acetone, tetrahydrofuran and chloroform, it has very good thermal stability and shows very good gas separation properties, in particular for mixtures where one of the components is CO2.22–25
Here, the preparation of ETS-10 MMMs based on PSF via casting/solvent evaporation technique (in contrast with our previously reported ETS-10/PSF MMMs prepared by spin coating)19 is studied. In addition, a more permeable fluorinated polymer, the polyimide 6FDA-6FpDA, is used as polymer matrix for the preparation of ETS-10 MMMs. In order to analyze the effect of the crystal size and morphology of the filler on the membrane performance, several ETS-10 crystals with different size and textural properties are synthesized and the MMMs are evaluated for separation of CO2/CH4 mixture. This mixture can be related to bio-methane upgrading, an application of special interest given the renewable character of such source of energy, whose use would contribute to reduce CO2 emissions.
A three-neck flask was equipped with a mechanical stirrer and a nitrogen inlet and outlet. The flask was filled with 20 mmol of 6FpDA diamine and 20 mL of N,N-dimehtylacetamide (DMAc), which was employed as the solvent. The mixture was stirred at room temperature until all the solid had dissolved. Then, the solution was cooled to 0 °C and the required amount of trimethylchlorosilane (TMSCl) (1 mol per mol amino group, 40 mmol) was slowly added, followed by the addition of pyridine (1 mol per mol amino group, 40 mmol). The solution was heated to room temperature and stirred for 15 min to ensure the formation of the silylated diamine in the appropriate cases. After this time, the solution was once more cooled to 0 °C, and 20 mmol of 6FDA was rapidly added along with 15 mL of DMAc. Finally, a small amount of 4-dimethylamine pyridine (DMAP) (0.1 mol per mol amino group, 4 mmol) was added followed by 5.0 mL of solvent. The reaction mixture was then stirred for 15 min at 0 °C after which the temperature was raised to room temperature and left overnight.
Cyclodehydration of the formed polyamic acid was accomplished by using an acetic anhydride (60 mmol)/Py (60 mmol) mixture. The reaction mixture was stirred at room temperature for 6 h followed by heating for a further hour at 60 °C. Afterwards, the flask was cooled down to room temperature and the resulting polymer solution was precipitated into 1000 mL of water, washed several times with water and extracted in a Sohxlet extractor with ethanol to remove traces of solvent and oligomers. The 6FDA-6FpDA polymer was dried overnight under vacuum at 200 °C in order to remove the occluded solvent. Yield over 91% was obtained.
000) and polyimide 6FDA-6FpDA. ETS-10 MMMs were prepared by the casting/solvent evaporation technique using chloroform as solvent. Firstly, 3.6 g and 4.2 g of chloroform (Sigma Aldrich, 99%) for PSF and 6FDA-6FpDA based MMMs, respectively, together with the amount of ETS-10 necessary to obtain the required loading (10–20 wt%) were mixed, keeping the amount of ETS-10 + polymer = 0.4 g. The polymer (PSF or 6FDA-6FpDA) was then added and the resulting dispersion was stirred overnight. The suspension was then sonicated with three intervals of 15 min, cast on a flat glass plate and then left overnight, partially covered to slow down the natural evaporation of solvent under ambient conditions. Once dried at room temperature, the films were placed for 24 h under 1 kPa pressure in a vacuum oven at 120 °C for PSF based MMMs and at 180 °C for 6FDA-6FpDA based MMMs to remove the remaining solvent.
The ETS-10 samples and MMMs based on 6FDA-6FpDA were also characterized by X-ray diffraction (XRD) at room temperature using a D-Max Rigaku diffractometer with a copper anode and a graphite monochromator to select Cu-Kα1 radiation (λ = 1.5418 Å).
Nitrogen adsorption–desorption isotherms were measured at 77 K using a porosity analyzer (TriStar 3000, Micromeritics Instrument Corp.). The samples were outgassed with a heating rate of 10 °C min−1 until 200 °C and maintained for 8 h. BET specific surface areas were measured from the adsorption branches in the relative pressure range of 0.05–0.25 and external surface areas were calculated using the t-plot method.
Fig. 2 and 3 and Table 1 show SEM images, X-ray diffraction patterns and textural properties, respectively, of the different samples selected for the preparation of the MMMs. Table 1 also shows the ETS-10 particle size, in both c and a = b directions.32
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| Fig. 2 SEM images of ETS-10 samples used for MMM preparation: (a) Ti2_180_48 h, (b) TiCl3_180_48 h, (c) TiCl3_180–230_48–2 h, (d) TiCl3_180–230_48–24 h. | ||
| ETS-10 sample | SBET (m2 g−1) | Sext (m2 g−1) | Particle size (μm) |
|---|---|---|---|
| a The first value corresponds to crystal size in direction c, and the second value to crystal size in directions a = b.32 | |||
| Conventional TiCl3_230_24 h | 289 ± 4 | 20 | 1.9 × 2.3a |
| Ti2_180_48 h | 206 ± 5 | 30 | 0.44 × 0.21a |
| TiCl3_180_48 h | 94 ± 0 | 59 | 0.08 ± 0.02 |
| TiCl3_180–230_48–2 h | 318 ± 5 | 42 | 1.2 ± 0.2 |
| TiCl3_180–230_48–24 h | 166 ± 3 | 41 | 1.9 ± 0.3 |
Sample Ti2_180_48 h (Fig. 2a) was synthesized with TiO2-anatase nanoparticles (25 nm), which led to a heterogeneous primary nucleation of ETS-10.5 This, together with its low solubility, dramatically reduced the availability of nutrients for growth, leading to small ETS-10 particles (0.44 × 0.21 μm). It is worth mentioning that at 180 °C it was not possible to obtain ETS-10 crystals with Ti1 (200–300 nm), since this Ti source needs higher temperatures to be dissolved. In general, when using the same synthesis conditions (i.e. 230 °C and 48 h), larger crystal particles were obtained with TiCl3 (see Table S1 and Fig. S1, ESI†), due to the promotion of crystal growth over nucleation when this more soluble Ti source was used.5
When the temperature was reduced to 180 °C and the molar gel was diluted (sample TiCl3_180_48 h), nanocrystals of 80 ± 20 nm were obtained (Fig. 2b) with the presence of amorphous gel detected by XRD (see Fig. 3). This fact could be due to the low temperature used, which was insufficient to dissolve all the nutrients for crystal growth. It is worth mentioning that this is the smallest particle size ever reported for this material.5,26,30,33 In sample Ti2_180_48 h, ETS-4 and TiO2-anatase impurities were also present (see Fig. 3).
To increase the crystallinity of the TiCl3_180_48 h sample, after 48 h at 180 °C the gel synthesis was heated up to 230 °C and maintained for 2 h (sample TiCl3_180–230_48–2 h, Fig. 2c) and 24 h (sample TiCl3_180–230_48–24 h, Fig. 2d). The increase in synthesis temperature to 230 °C increased the particle size to 1.2 ± 0.2 μm and 1.9 ± 0.3 μm after 2 h and 24 h, respectively. The crystallinity and porosity of these two samples were also higher than those for the TiCl3_180_48 h sample (see Fig. 3 and Table 1), indicating that when TiCl3 is used temperatures higher than 180 °C are needed to crystallize the titanium and silicon nutrients. SEM images of these samples (Fig. 2c and d) show particles consisting of polycrystalline aggregates that became twin crystals after 24 h, different from those of the TiCl3_230_24 h sample (Fig. S1b, ESI†) which exhibits the typical truncated pyramidal crystal shape. The particles in Fig. 2c and d show an evident surface roughness that could be due to two reasons. Firstly, the dilution of the initial synthesis mixture resulting in crystal clusters, as previously reported.4 Secondly, the presence of ETS-10 nanocrystals (Fig. 2b) generated at the 180 °C stage that act as seeds when the temperature is increased to 230 °C and grow close each other, creating polycrystalline particles.
The external surface of these samples was in accordance with their particle size and roughness. The TiCl3_180_48 h sample had the highest external surface area (59 m2 g−1) due to its having the smallest particle size (80 nm) in addition to the particle agglomeration that led to capillarity condensation between the crystals. Furthermore, samples TiCl3_180–230_48–2 h and TiCl3_180–230_48–24 h have extra roughness due to the intercrystalline regions, leading to high external specific surface areas (41–42 m2 g−1). To increase this external area value, other strategies such as postsynthesis treatment with hydrogen peroxide under microwave irradiation has been reported,34 creating mesopores within the ETS-10 structure that increased the external surface area of this material up to 70 m2 g−1.
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| Fig. 4 SEM images of cross-sections of 10 wt% MMMs based on PSF with different ETS-10 samples, (a) Ti2_180_48 h, (b) TiCl3_180_48 h, (c) TiCl3_180–230_48–2 h, (d) TiCl3_180–230_48–24 h. | ||
Table 2 and Fig. 5 show the gas separation results for the CO2/CH4 mixture of 10 wt% MMMs based on PSF with different ETS-10 samples. For Ti2_180_48 h and TiCl3_180_48 h MMMs, the ETS-10 agglomerations observed by SEM created voids between the particles that could explain the decrease in CO2/CH4 selectivity. In addition, the slight decrease in CO2 permeability could be due to the low porosity of TiCl3_180_48 h sample and the presence of non-porous anatase as impurity in the Ti2_180_48 h sample. MMMs using samples TiCl3_180–230_48–2 h and TiCl3_180–230_48–24 h as fillers increased both their CO2 permeability and CO2/CH4 selectivity in comparison with pure polymer. This can be explained by the fact that, in addition to the high porosity of these fillers and the good filler–polymer interaction, ETS-10 preferentially adsorbs CO2 over CH4,35 probably because of the significantly greater quadrupole moment and polarizability of CO2 molecules. Furthermore, adsorbed CO2 is expected to reduce the CH4 permeation by hindrance, resulting in overall CO2 selectivity in CO2/CH4 mixtures.17 Thus, because of two concomitant effects, i.e., the diffusion and sorption paths created in the membrane when ETS-10 crystals are added and the optimized filler–polymer contact, the pursued trend of increasing both the permeability and selectivity with the addition of the filler was achieved.
| Sample | CO2 permeability (Barrer) | Selectivity CO2/CH4 |
|---|---|---|
| Pure PSF | 6.1 ± 0.2 | 31 ± 1 |
| Ti2_180_48 h | 5.4 | 28 |
| TiCl3_180_48 h | 5.6 | 29 |
| TiCl3_180–230_48–2 h | 7.8 | 38 |
| TiCl3_180–230_48–24 h | 7.2 | 40 |
| Measurement | CO2 permeability (Barrer) | CO2/CH4 selectivity |
|---|---|---|
| a The standard deviation was calculated from two different membranes.b The standard deviation was calculated from membranes prepared with different solvents (dichloromethane, tetrahydrofuran, N,N-dimethylacetamide, N,N-dimethylformamide and acetone). | ||
| Binary mixture (ΔP = 205 kPa) | 96 ± 1a | 56 ± 3a |
| Single gas (ΔP = 205 kPa) | 85.1 | 41.3 |
| Single gas “time lag” method (literature)22 (ΔP = 101 kPa) | 73 ± 6b | 44 ± 2b |
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| Fig. 6 SEM images of cross-sections of TiCl3_180–230_48–2 h MMMs based on 6FDA-6FpDA with different filler loadings, (a) 10 wt%, (b) 20 wt%. | ||
The XRD pattern of the MMMs (Fig. 7) matches the pattern of the filler, and the signal peaks related to ETS-10 increased with the filler loading, confirming that the particles preserved their structure inside the polymeric matrix.
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| Fig. 7 XRD patterns of TiCl3_230_24 h ETS-10, polyimide 6FDA-6FpDA and TiCl3_180–230_48–2 h ETS-10 MMMs (10 and 20 wt% loading). | ||
Compared to bare polymer, ETS-10 MMMs based on 6FDA-6FpDA with 10 wt% loading showed an improvement in the CO2 permeability from 96 ± 1 to 125 ± 1 Barrer, with a slight decrease in CO2/CH4 selectivity from 56 ± 3 to 51 ± 2 (Fig. 5). The fact that CO2/CH4 selectivity did not improve with the addition of ETS-10 could be explained from the selectivity value reported for ETS-10 for CO2/N2 mixtures (similar to CO2/CH4 mixtures) using a continuous ETS-10 membrane.17 Although defects along the continuous ETS-10 membrane could modify this value, the reported CO2/N2 selectivity was 10.8, much lower than that for the 6FDA-6FpDA polymer. In the case of the MMMs, the defects may correspond to the ETS-10-6FDA-6FpDA polymer gaps or non-selective transport pathways through the intercrystalline spaces of the ETS-10 particles, since the ideal CO2/CH4 selectivity for ETS-10 crystals (calculated from adsorption data in the Henry's law region using the Langmuir equation) is 357 at 25 °C.35 When higher amounts of this filler were added (20 wt%), the permeability increased to 183 Barrer but the CO2/CH4 selectivity dramatically decreased to 13, due to the increase in the formation of non-selective filler–polymer voids caused by particle agglomeration at high loadings. It can be said that the presence of defects in 6FDA-6FpDA based MMMs do not compensate, in terms of separation performance, the enhancement achieved in the filler–polymer interaction by modification of the textural properties of the filler. In any event, the CO2/CH4 separation performance of pure polymer and 10 wt% ETS-10 MMM are represented in the 2008 Robeson upper bound (Fig. 5), where the results obtained with these membranes are close to the commercially attractive zone.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: 10.1039/c5ra20172a |
| This journal is © The Royal Society of Chemistry 2015 |