Literature DB >> 35910293

Combined Superbase Ionic Liquid Approach to Separate CO2 from Flue Gas.

Adam J Greer1, S F Rebecca Taylor1, Helen Daly1, Johan Jacquemin2,3, Christopher Hardacre1.   

Abstract

Superbase ionic liquids (ILs) with a trihexyltetradecylphosphonium cation and a benzimidazolide ([P66614][Benzim]) or tetrazolide ([P66614][Tetz]) anion were investigated in a dual-IL system allowing the selective capture and separation of CO2 and SO2, respectively, under realistic gas concentrations. The results show that [P66614][Tetz] is capable of efficiently capturing SO2 in preference to CO2 and thus, in a stepwise separation process, protects [P66614][Benzim] from the negative effects of the highly acidic contaminant. This results in [P66614][Benzim] maintaining >53% of its original CO2 uptake capacity after 30 absorption/desorption cycles in comparison to the 89% decrease observed after 11 cycles when [P66614][Tetz] was not present. Characterization of the ILs post exposure revealed that small amounts of SO2 were irreversibly absorbed to the [Benzim]- anion responsible for the decrease in CO2 capacity. While optimization of this dual-IL system is required, this feasibility study demonstrates that [P66614][Tetz] is a suitable sorbent for reversibly capturing SO2 and significantly extending the lifetime of [P66614][Benzim] for CO2 uptake.
© 2022 The Authors. Published by American Chemical Society.

Entities:  

Year:  2022        PMID: 35910293      PMCID: PMC9326967          DOI: 10.1021/acssuschemeng.2c01848

Source DB:  PubMed          Journal:  ACS Sustain Chem Eng        ISSN: 2168-0485            Impact factor:   9.224


Introduction

Gas capture sorbents such as alkanolamines, metal–organic frameworks, porous liquids, and ionic liquids (ILs) are being increasingly studied in the literature for CO2 uptake to combat rising greenhouse gas emissions.[1−6] While CO2 emissions are subject to legislation in the UK, in line with achieving net zero by 2050, other components of waste gas streams such as SO2 and nitrogen oxides (NO) also require removal due to their contribution to acid rain and smog formation.[7] For CO2 removal from flue gas streams, aqueous alkanolamine scrubbers are the benchmark carbon capture technology commercially available. The production and regeneration of these sorbents are energy intensive, and the loss of the amine sorbent during operation, due to degradation and evaporation, brings additional environmental considerations along with the production of highly corrosive waste solutions.[8] In terms of CO2 capture, the addition of contaminants such as SO2 has been demonstrated to degrade current capture sorbents like alkanolamines; however, consideration of the effect of such impurities has not been widely considered in the literature when investigating the viability of new CO2 capture sorbents.[9−11] Currently, approximately 85% of power plant desulfurization occurs via a wet limestone–gypsum process which has a high desulfurization rate and a low cost of operation.[8,12,13] This process requires waste water treatment, and while gypsum (formed as a by-product) has a number of applications such as in wallboard manufacturing and the cement industry, globally, a large proportion goes to landfill.[14,15] The efficiency of such desulfurization processes (and other purification stages) before CCS (Carbon Capture and Storage) significantly impacts the sorbent lifetime and the overall process efficiency and cost. ILs have received substantial interest for gas capture due to a tunable structure through the pairing of different cations and anions and favorable physical properties (high thermal stability, low melting point, and low vapor pressure).[16] In addition, reported calculations show reductions in energy consumption (lower temperature/pressure sorbent regeneration conditions) and overall costs for IL-based gas separation processes, compared to commercial amine-based CO2 absorbents, which are additional drivers for their use.[17,18] The ability of an IL to interact either physically or chemically with different gases allows the process to be tailored to optimize the gas uptake capacities through a knowledge of the absorption enthalpies and physiochemical properties of the ILs.[19−21] Therefore, the available data can now be used to identify a wide range of structure–activity relationships for selective gas capture by ILs.[17,22−24] In the majority of cases, the anion has been shown to have the largest effect on gas uptake capacities, where there is now an increasing trend in investigating the consequence of altering the anion basicity.[20,25,26] In particular, superbase ILs (SBILs) with aprotic heterocyclic anions have been shown to reversibly capture large amounts of CO2 (>1 nCO2/nIL) with minimal increases in viscosity,[27,28] an important consideration in the industrial application of ILs. For SBILs, where it has been demonstrated that the basicity of the anion can affect the absorption enthalpies, the presence of acidic gases such as SO2 in the feed can significantly affect the recyclability of the sorbent.[29−32] The effect of the anion on the capture of CO2 and SO2 is displayed in Table for two SBILs: trihexyltetradecylphosphonium benzimidazolide, [P66614][Benzim], and trihexyltetradecylphosphonium tetrazolide, [P66614][Tetz]. [P66614][Benzim] has been used in a series of studies investigating the effect of flue gas contaminants on CO2 uptake and was also shown to capture significantly more CO2 per mole of IL in comparison to [P66614][Tetz] (1.20 vs 0.08 nCO2/nIL) due to a higher absorption enthalpy (−52.1 vs −19.1 kJ·mol–1).[20,27,31−34] Importantly, when SO2 capture is considered, both ILs can absorb large amounts. However, [P66614][Benzim] does so irreversibly, which has been shown to have a negative effect on its ability to simultaneously absorb CO2.[32,33] In contrast, a small residue following desorption (0.06 nSO2/nIL) was reported for [P66614][Tetz] after exposure to 0.2 vol % SO2 which may be due to a weaker binding affinity when compared to [P66614][Benzim] (−89.4 vs −123.9 kJ·mol–1).[31−33] However, a study of the recyclability of [P4442][Tetz] showed that the working absorption capacity remained constant.[31]
Table 1

CO2 Capacity, SO2 Capacity, and Absorption Enthalpy of the Two SBILs Investigated in This Work; Trihexyltetradecylphosphonium Benzimidazolide, [P66614][Benzim], and Trihexyltetradecylphosphonium Tetrazolide [P66614][Tetz]

The differing absorption enthalpies of these SBILs toward CO2 and SO2 could allow the possibility of using the two SBILs in series for stepwise gas separation, with [P66614][Tetz] used to selectively absorb SO2. In this case, [P66614][Tetz] acts as a scrubber and extends the lifetime of [P66614][Benzim] for the reversible capture of CO2. Previous studies on the gas absorption of SO2 by [P66614][Benzim] showed that in the presence of realistic flue gas amounts of SO2 (0.2 vol %), an 89% decrease in CO2 capacity was observed over 11 absorption/desorption cycles.[32] Herein, the feasibility of using [P66614][Tetz] with [P66614][Benzim] in a dual-IL system has been investigated to assess the effect on the lifetime and recyclability of the [P66614][Benzim] sorbent for CO2 uptake. This study has utilized the previously developed mass spectrometry-based gas absorption rig,[32-34] with the ILs after exposure characterized using NMR and elemental analyses to determine their recyclability. This paper is a feasibility study for the use of ILs in a stepwise separation process and shows [P66614][Tetz] to increase the lifetime of [P66614][Benzim] as a CO2 capture sorbent.

Experimental Section

Materials

Trihexyltetradecylphosphonium chloride (97.7 wt %, CAS: 258864-54-9) was obtained from IoLiTec; benzimidazole (98 wt %, CAS: 51-17-2) and tetrazole (CAS: 288-94-8) were purchased from Sigma-Aldrich. [P66614][Superbase] was prepared using a previously reported two-step synthesis method.[27] The structure and purity of the ILs, after synthesis and post-exposure, were analyzed using 1H NMR and 13C NMR with a Bruker AVANCE II 500 MHz Ultra shield Plus spectrometer and carried out as neat ILs in the presence of a glass capillary insert containing DMSO-d6, purchased from Cambridge Isotope Laboratories Inc. (CAS: 2206-27-1). The halide content was determined to be <5 ppm using a silver nitrate test, and water content was measured to be <0.1 wt % using a Metrohm 787 KF Titrino Karl Fischer machine. The following gases were obtained from BOC: argon (99.998%, CAS: 7440-37-1), carbon dioxide (99.99%, CAS: 124-38-9), and sulfur dioxide (1% in argon, CAS: 7446-09-5). The IL samples post exposure to the gases were stored in an argon-filled glovebox before analysis. Elemental analysis was carried out using a Thermo Scientific Flash 2000 elemental analyzer.

Methods

In previous work, a novel gas absorption technique utilizing mass spectrometry was developed to allow the study of mixed component gas feeds that resemble realistic flue gas conditions.[32−34] This experimental setup was modified, herein, to allow the inclusion of two reactors connected in series, and this is shown in Figure . ∼2 g (±0.1 mg) of [P66614][Benzim] and [P66614][Tetz] were weighed out separately in an argon-filled glovebox and transferred into individual temperature-controlled glass reactors. A series of absorption and desorption cycles were then carried out consisting of a 2 h absorption period at 22 °C (±0.05 °C) and 1 atm (±0.05 atm) under feed conditions of 14% CO2 in Ar or 14% CO2 + 0.2% SO2 in Ar, followed by a 2 h desorption step at 90 °C under Ar.
Figure 1

Schematic depicting the gas absorption rig used in this work.

Schematic depicting the gas absorption rig used in this work. To prevent the exposure of [P66614][Benzim] to SO2 during the desorption step, a four-way valve was used to direct the outlet from the reactor containing [P66614][Tetz] to the vent, while the outlet of [P66614][Benzim] was directed to the mass spectrometer. Initially, a baseline for the absorption of CO2 by the two ILs was found by flowing a feed of 14% CO2 in Ar through both reactors consecutively. Six cycles were performed, yielding an average CO2 uptake of 0.77 nCO2/nIL, agreeing with previously published work. Three cycles with a feed of 14% CO2 in Ar were then carried out after every five consecutive 14% CO2 + 0.2% SO2 in Ar cycles to monitor the CO2 capacity of the ILs. The breakthrough curve from the mass spectra was used to calculate the CO2 uptake with an error of ±0.04 nCO2/nIL.

Results and Discussion

The gas absorption rig developed was used to determine whether the use of [P66614][Tetz] as a SO2 scrubber would protect the CO2 recyclability of [P66614][Benzim] under a realistic gas feed (14% CO2 + 0.2% SO2 in Ar). It should be noted that the design of the scrubber was not optimized to maximize SO2 removal in this feasibility study. The results are shown in Figure and are presented in comparison to earlier work without the presence of the [P66614][Tetz] scrubber, where it was shown that SO2 irreversibly absorbs to the [Benzim]− anion resulting in the formation of an irreversibly absorbed sulfur species and deactivation of the IL to CO2 capture.[32]
Figure 2

CO2 capacity of [P66614][Benzim] with (dashed bars) and without the presence of [P66614][Tetz] (filled bars) after 30 cycles of 2 h absorption at 22 °C under a feed of 14% CO2 and 0.2% SO2 in Ar and a 2 h desorption at 90 °C under Ar. The diamonds depict a moving average of subsequent CO2 uptake values, with an error of ±0.04 nCO2/nIL. Data for the CO2 capacity of [P66614][Benzim] without [P66614][Tetz] is available from ref (32).

CO2 capacity of [P66614][Benzim] with (dashed bars) and without the presence of [P66614][Tetz] (filled bars) after 30 cycles of 2 h absorption at 22 °C under a feed of 14% CO2 and 0.2% SO2 in Ar and a 2 h desorption at 90 °C under Ar. The diamonds depict a moving average of subsequent CO2 uptake values, with an error of ±0.04 nCO2/nIL. Data for the CO2 capacity of [P66614][Benzim] without [P66614][Tetz] is available from ref (32). Initial observations revealed that the CO2 capacity of [P66614][Benzim] dropped from 0.77 to 0.71 nCO2/nIL after one cycle under the CO2 + SO2 in Ar feed. As this is outside the error of the measurement (0.04 nCO2/nIL), the decrease could either be attributed to the influence of SO2 on [P66614][Benzim] and/or the loss of a small CO2 contribution from [P66614][Tetz] due to the stronger absorption enthalpy of SO2. This is because the initial CO2 only value of 0.77 nCO2/nIL includes contributions from both [P66614][Benzim], and [P66614][Tetz]. As the number of cycles increases, both ILs are exposed to increasing amounts of SO2, and it can be seen that the CO2 capacity of [P66614][Benzim] decreases further. For this 1:1 ratio of [P66614][Tetz] to [P66614][Benzim] (by mass), the decreasing CO2 capacity of [P66614][Benzim] suggests that the reactor containing [P66614][Tetz] was unable to fully remove SO2 from the mixed gas feed and allowed the exposure of a reduced amount of SO2 to interact with [P66614][Benzim]. After 11 absorption/desorption cycles, the CO2 capacity of [P66614][Benzim] had reduced to 0.54 nCO2/nIL, a 30% decrease. Conversely, when the gas feed was not scrubbed by [P66614][Tetz], an 89% decrease (to 0.09 nCO2/nIL) in the CO2 capacity of [P66614][Benzim] was observed, demonstrating the significant impact [P66614][Tetz] has on extending the lifetime of the sorbent.[32] As such, a total of 30 cycles were carried out on the new system, after which it was found that [P66614][Benzim] still maintained >53% of its original capacity (0.41 nCO2/nIL). For comparison, the theoretical maximum CO2 uptake by the benchmark alkanolamine sorbent is 0.5 nCO2/nMEA.[35] The CO2 uptake capacity demonstrated herein shows potential for dual-IL systems even after numerous regenerative treatments. Additionally, it can be seen that after 21 cycles, the CO2 uptake began to stabilize, suggesting that an equilibrium point was reached. It is possible that at these extremely low concentrations of SO2 and relatively much higher concentrations of CO2, CO2 can compete for the absorption sites within the [P66614][Benzim] IL. Previous work with NO and SO2 demonstrated that acidic gases can physically and chemically interact with both N-sites on the [Benzim]− anion, suggesting that under these conditions SO2 could feasibly be strongly absorbed to one N-site, while CO2 is more weakly absorbed on the second N-site and competes with the lower SO2 concentration in the feed.[33,34] It is important to note that similar studies have shown that in the presence of the [Tetz]− anion, SO2 can interact on multiple N-sites. In this case, the absorption enthalpies decrease as subsequent absorption sites are filled.[29] Further analysis of the results revealed fluctuations between cycles in the calculated CO2 capacities; however, the overall trend was still exposed. The results were plotted with a moving average (indicated by diamonds in Figure ), and this showed that the variations decrease as the number of cycles increases. After every five CO2/SO2 absorption/desorption cycles, three CO2 only cycles were performed, and the average CO2 uptake is displayed in Figure S1. This shows further agreement with the experimental results, where a decrease in CO2 uptake occurs, followed by stabilization after 20 CO2/SO2 cycles (0.41 nCO2/nIL). The theoretical absorption enthalpies for [P66614][Tetz] suggest that this IL will preferably absorb SO2 (−89.4 kJ·mol–1) over CO2 (−19.1 kJ·mol–1).[20,31] To explore this, the mass spectrometry-derived breakthrough curves for SO2 are plotted in Figure S2. This shows that for at least the first 20 cycles, an extremely low (unmeasurable) amount of SO2 exits the reactors, indicating that the vast majority of the SO2 present in the feed is being captured by both ILs. Over the next 10 cycles, the breakthrough of SO2 was observed indicating accumulation of SO2 absorbed in the IL and that a saturation point had been reached for some of the absorption sites. Interestingly, this correlates with an equilibrium being reached in terms of CO2 uptake, suggesting that there is competition for the absorption sites. At this stage, it is also important to note that during one absorption cycle, [P66614][Tetz] is exposed to a calculated 0.12 nSO2/nIL and therefore does not exceed the overall capacity of the IL (0.87 nSO2/nIL).[31] With optimization of the scrubber design, for example, reducing the bubble size, higher levels of SO2 uptake would be achievable at lower amounts of IL, which would be favorable to the process costs. Subsequent characterization of [P66614][Tetz] (below) indicates that the absorption of SO2 is reversible and demonstrates that the detection of increased amounts of SO2 by mass spectrometry is not caused by incomplete regeneration of the sorbent but may be due to a loss of efficiency due to the ability of [P66614][Tetz] to absorb gases on multiple absorption sites with differing binding affinities.[31,36] The influence of residual water, present in either the ILs or gas feed, was also considered as a potential mode of deactivation of the ILs as this can lead to the formation of further acidic gas species or protonation of the IL anion.[37] However, no significant impact from water was observed in this work. The ILs were subsequently removed from the gas absorption rig after 30 cycles and characterized using NMR and elemental analyses. 1H NMR indicates a small downfield shift in the protons attached to the [Benzim]− anion (Figures and S3) from 6.30/6.88/7.28 to 6.41/7.00/7.48 ppm. This agrees with previous literature and indicates the irreversible absorption of a small amount of SO2, as expected from the gas absorption rig results.[30,32] In the case of the [Tetz]− anion, a downfield shift was observed from 7.72 to 7.97 ppm, as well as a broadening of the peak. These studies have noted that there is often a desorption residue (0.06 nSO2/nIL) for [P66614][Tetz], indicating the irreversible absorption of a small amount of SO2 and explaining the small chemical shift changes; however, a significantly high recyclability was still observed.[29,31] The 13C NMR spectra are shown in Figure S3 where shifts were also found for the anionic peaks, agreeing with these findings.
Figure 3

1H NMR spectra of [P66614][Benzim] before (a) and after (b) exposure and [P66614][Tetz] before (c) and after (d) exposure to the CO2 and SO2 absorption cycles.

1H NMR spectra of [P66614][Benzim] before (a) and after (b) exposure and [P66614][Tetz] before (c) and after (d) exposure to the CO2 and SO2 absorption cycles. Elemental analysis (Table S1) was performed on both ILs before and after exposure in the gas absorption rig, where [P66614][Benzim] was found to show a small increase in the sulfur content (to 1.64 wt %). This is in comparison to 4.56 wt % that was found in previous work after 11 cycles with no [P66614][Tetz] scrubber, demonstrating a 64% decrease in the sulfur content in [P66614][Benzim] after 30 cycles.[32] In contrast, for [P66614][Tetz], no change was observed after exposure, in agreement with the indication that the SO2 is reversibly absorbed in this IL. It should be noted that a desorption residue has been observed by other authors and in the NMR results, herein, but was not observed in the elemental analysis results.[31] It is possible that this is a result of the uncertainty from the elemental analyzer used in this work (u = 0.3 wt %) as the contamination is expected to be low from previous studies.[31] The post-exposure characterization reveals that the use of [P66614][Tetz] as a reversible scrubber to remove SO2 from the feed and protect [P66614][Benzim] was not completely effective, with the results indicating the incorporation of a small amount of SO2 into the structure of [P66614][Benzim] and a subsequent decrease in the CO2 capacity. Optimization of the dual-IL system in terms of the ratio of [P66614][Tetz] to [P66614][Benzim] and the flow rate/residence time of the gases in the ILs could feasibly increase the SO2 uptake and, therefore, the CO2 uptake and lifetime of [P66614][Benzim], improving the overall efficiency of the process for longer-term operation. Furthermore, stepwise processes for the capture and separation of SO2 and CO2 have been reported to save ∼50% of the energy compared to simultaneous separation processes.[38] In addition, such a dual-IL system, with stepwise separation of SO2 and CO2 from flue gas, could provide pure gas streams (albeit diluted in an inert gas) during desorption and regeneration of the IL. The pure SO2 gas streams could be utilized as feedstocks for processes such as conversion to elemental sulfur and/or used in sulfuric acid production,[39] and the CO2 stream could be used in the production of chemicals and fuels such as urea, a major agricultural fertilizer, or methane (dry reforming or hydrogenation), as well as in the food and beverage industries.[40] In situ utilization of gases absorbed (and activated) by ILs is also a continually developing research area.[41−45] However, barriers to the deployment of IL systems for gas capture include their high viscosity (with consideration to viscosity changes upon gas absorption required) and the cost of IL production on an industrial scale. In the development of such task-specific ILs for gas separation processes, the toxicology and environmental impact of the chosen ILs require evaluation alongside the energy consumption and techno-economic calculations/modeling of the desired process.[4,46] This technology has the potential to be applied to NO removal, as well as SO2. A number of ILs, including [P66614][Tetz], have been shown to display large “working” capacities for NO, presenting an opportunity for removing both contaminants simultaneously through multisite absorption capability.[36,47−51] However, it is essential to study conditions that are representative of real-world environments to assess the impact of realistic amounts of flue gas contaminants on the ability of IL sorbents to reversibly capture CO2.[32−34] Gas capture in thin films of ILs, such as [P66614][Benzim], is also being investigated as studies have shown that their behavior differs in comparison to bulk solution.[52] Finally, it is important to consider the advantages and disadvantages that ILs present in comparison to other CO2 capture solvents for a commercial process, both in terms of performance and also economic feasibility, presenting an area for future exploration.[5,16]

Conclusions

This work has demonstrated that the use of [P66614][Tetz] as a SO2 scrubber enables the extended lifetime of a CO2 capture sorbent, [P66614][Benzim], where after 30 absorption/desorption cycles, >53% of its original CO2 uptake capacity remains. Further design engineering offers the potential to limit the degradation of [P66614][Benzim] by increasing the efficiency of SO2 removal. Deactivation of [P66614][Benzim] to the absorption of CO2 was characterized using NMR and elemental analyses, showing the irreversible uptake of sulfur into the IL, blocking the active sites. However, analysis of [P66614][Tetz] showed that this IL was largely unaffected by SO2 absorption, offering the capability of reversibly absorbing SO2 under the studied conditions. By tuning the basicity of the anion ([Tetz]−) to initially and selectively capture SO2, an anion with a higher affinity for gas capture ([Benzim]−) was able to be used to remove CO2 from a multicomponent gas feed. Anion effects have been well investigated for gas capture, but this is the first time, to the best of the authors’ knowledge, that a dual system has been proposed and investigated. However, it is also important to consider the effect of the cation on basicity by tuning the cation–anion interactions, and this offers an area for continued exploration.[53]
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