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Oxidative Desulfurization of Gasoline by Ionic Liquids Coupled with Extraction by Organic Solvents

Abstract

In this work, desulfurization of real fluidized catalytic cracking (FCC) gasoline was investigated in dual steps; first in oxidative desulfurization (ODS) using imidazolium and pyrrolidonium based Brønsted acidic ionic liquids (ILs) as solvent and catalyst and hydrogen peroxide as oxidant. In second step, extractive desulfurization took place using organic solvents of furfural, furfural alcohol and ethylene glycol. Variety of factors such as temperature, time, mass ratio of oil/ILs and regeneration and recycling of ILs, multiple-step desulfurization of ILs and organic solvents and solvent/oil ratio were also investigated. The S-content was significantly decreased to ca. 18 ppm from initial S-content of 260 ppm with a total S-removal of ca. 95% in one-step ODS using pyrrolidonium based ILs coupled with five-step extraction desulfurization (EDS) using furfural alcohol as extractant. This work shows that oxidative desulfurization using ionic liquids coupled with extractive desulfurization using organic solvents is a potential method to produce clean gasoline.

Keywords:
gasoline; oxidative desulfurization; extractive desulfurization; ionic liquids; ultra-clean fuel oil


Introduction

The emission of sulfur (S) during combustion from light fuel oils, coupled with increasing automobiles has heightened concern on environmental pollution. The sustained emission of these gases leads to air pollution, acid rain, and global climate change as well as increases health risk from continuous exposure to this smog. Economically, it affects the catalytic converter emission of vehicles resulting in inefficient fuel utilization and poor performance. In 1998, the European Union instituted legislations to monitor the S-limits in fuel oils by setting up mandatory S-content limit to be less than 10 ppm or negligible level.11 Abdalla, Z. E. A.; Li, B.; Tufail, A.; J. Ind. Eng. Chem. 2009, 15, 780.

2 Seeberger, A.; Jess, A.; Green Chem. 2010, 12, 602.
-33 Abro, R.; Abdeltawab, A. A.; Al-Deyab, S. S.; Yu, G.; Qazi, A. B.; Gao, S.; Chen, X.; RSC Adv. 2014, 67, 35302. In March 2014, the United States Environmental Protection Agency proposed new standards to further reduce the S-content from the current 30 to 10 ppm. In recent years, Japan has also made significant efforts to reduce the S-content from 500 to 50 ppm. Some European countries including Denmark and Germany have imposed taxes on fuel oil refineries that fail to meet the standard (Figure 1 shows the maximum gasoline S-limits in different regions).44 Ibrahim, J. J.; Gao, S.; Abdeltawab, A. A.; Al-Deyab, S. S.; Yu, L.; Yu, G.; Chen, X.; Yong, X.; Sep. Sci. Technol. 2015, 50, 1166. The goal, of course, is to realize ultra-low, possibly zero, S-content in gasoline in the not-too-distant future.

Figure 1
Proposed sulfur limitations in gasoline in different countries.33 Abro, R.; Abdeltawab, A. A.; Al-Deyab, S. S.; Yu, G.; Qazi, A. B.; Gao, S.; Chen, X.; RSC Adv. 2014, 67, 35302.,55 http://www.unep.org/transport/pcfv/PDF/Session3-Asia-TanDagang-MEPChina.pdf, accessed in December 2015.
http://www.unep.org/transport/pcfv/PDF/S...

Hydrodesulfurization (HDS) is the well-established method employed in industry for this regard, where S-compounds are converted into hydrogen sulfide (H2S) in the presence of catalyst at elevated temperatures and pressures. HDS has some disadvantages such as the need for expensive catalysts, high temperature (300 to 340 °C) and high pressure (20 to 100 atm of H2). More importantly, aliphatic thiols and sulfides can effectively be removed in HDS while thiophene and its derivatives are not easily removed because of the steric hindrance for catalysis.66 Gao, S.; Chen, X.; Abro, R.; Abdeltawab, A. A.; Al-Deyab, S. S.; Yu, G.; Ind. Eng. Chem. Res. 2015, 54, 9421. Therefore, some alternative techniques such as adsorption desulfurization (ADS),77 Hernández-Maldonado, A. J.; Yang, R. T.; Ind. Eng. Chem. Res. 2003, 42, 123.

8 Hernández-Maldonado, A. J.; Yang, F. H.; Qi, G.; Yang R. T.; Appl. Catal., B 2005, 56, 111.
-99 Baeza, P.; Aguila, G.; Gracia, F.; Araya, P.; Catal. Commun. 2008, 9, 751. extraction desulfurization (EDS),1010 Jiang, W.; Zhu, W.; Li, H.; Wang, X.; Yin, S.; Chang, Y.; Li, H.; Fuel 2015, 140, 590.

11 Jiang, W.; Zhu, W.; Chang, Y.; Chao, Y.; Yin, S.; Liu, H.; Zhu, F.; Li, H.; Chem. Eng. J. 2014, 250, 48.
-1212 Ko, N. H.; Lee, J. S.; Huh, E. S.; Lee, H.; Jung, K. D.; Kim, H. S.; Cheong, M.; Energy Fuels 2008, 22, 1687. oxidation desulfurization (ODS),1313 Zhu, W.; Dai, B.; Wu, P.; Chao, Y.; Xiong, J.; Xun, S.; Li, H.; Li, H.; ACS Sustainable Chem. Eng. 2015, 3, 186.,1414 Zhu, W.; Wang, C.; Li, H.; Wu, P.; Xun, S.; Jiang, W.; Chen, Z.; Zhao, Z.; Li, H.; Green Chem. 2015, 17, 2464. and biodesulfurization (BDS)1515 Shan, G.; Xing, J.; Zhang, H.; Liu, H.; Appl. Environ. Microbiol. 2005, 71, 4497.,1616 Monticello, D. J.; Curr. Opin. Biotechnol. 2000, 11, 540. are sought in order to complement the HDS process. ODS is more competitive and efficient in removing the thiophenic S-compounds under mild conditions with low costs.1717 Alessandro, N.; Tonucci, L.; Bonetti, M.; Deo, M. D.; Bressan, M.; Morvillo, A.; New J. Chem. 2003, 27, 989.

18 Liu, S. Z.; Wang, B. H.; Cui, B. C.; Sun, L. L.; Fuel 2008, 87, 422.
-1919 Schmitz, C.; Datsevitch, L.; Jess. A.; Chem. Eng. Sci. 2004, 59, 2821. The use of molecular organic solvents such as dimethylsulfoxide (DMSO), dimethylformamide (DMF) and acetonitrile in ODS has been patented; some problems, however, exist in employing these organic solvents such as loss, contamination, regeneration, recycling and safety issues stemming from the volatile nature of organic solvents.2020 Zannikos, F.; Lois, E.; Stournas. S.; Fuel Process. Technol. 1995, 42, 35.

21 Otsuki, S.; Nonaka, T.; Takashima, N.; Qian, W. H.; Ishihara, A.; Imai, T.; Kabe, T.; Energy Fuels 2000, 14, 1232.

22 Ramírez-Verduzco, L. F.; Torres-García, E.; Gómez-Quintana, R.; González-Peña, V.; Murrieta-Guevara, F.; Catal. Today 2004, 98, 289.

23 Campos-Martin, J. M.; Capel-Sanchez, M. C.; Perez-Presas, P.; Fierro, J. L. G.; J. Chem. Technol. Biotechnol. 2010, 85, 879.

24 Sobati, M. A.; Dehkordi, A. M.; Shrahokhi, M.; Fuel Process. Technol. 2010, 91, 1386.
-2525 Shiraishi, Y.; Tachibana, K.; Hirai, T.; Komasawa, I.; Ind. Eng. Chem. Res. 2002, 41, 4362.

Recently, ionic liquids (ILs) have attracted increasing attention thanks to their desirable physicochemical properties such as negligible volatility, easy alteration of cation/anion structure for specific applications, high thermochemical stability and remarkable ability in dissolving organic/inorganic compounds. With wide-ranging applications in separation technology, nanotechnology, catalysis, electrochemistry, etc., ILs are being acclaimed as "green" and "designer" solvents.2626 Aquino, A. S.; Bernard, F. L.; Vieira, M. O.; Borges, J. V.; Rojas, M. F.; Vecchia, F. D.; Ligabue, R. A.; Seferin, M.; Menezes, S.; Einloft, S.; J. Braz. Chem. Soc. 2014, 25, 2251.

27 Zhang, M.; Li, M.; Chen, Q.; Zhu, W.; Li, H.; Yin, S.; Li, Y.; Li, H.; RSC Adv. 2015, 93, 76048.
-2828 de Souza, M. O.; J. Braz. Chem. Soc. 2014, 25, 2140. Several ILs have been studied as solvent in EDS for S-removal from fuel oils such as [1-butyl-3-methylimidazolium (Bmim)]PF6,2929 Zhang, S. G.; Zhang, Z. C.; Green Chem. 2002, 4, 376.,3030 Zhang, S. G.; Zhang, Q. L.; Zhang, Z. C.; Ind. Eng. Chem. Res. 2004, 43, 614. [Bmim]BF4,2929 Zhang, S. G.; Zhang, Z. C.; Green Chem. 2002, 4, 376.,3030 Zhang, S. G.; Zhang, Q. L.; Zhang, Z. C.; Ind. Eng. Chem. Res. 2004, 43, 614. [1-methyl-3-octylimidazolium (Omim)]BF4,3131 10. Alonso, L.; Arce, A.; Francisco, M.; Soto, A.; J. Chem. Thermodyn. 2008, 40, 966.,3232 Chu, X. M.; Hu, Y. F.; Li, J. G.; Liang, Q. Q.; Liu, Y. S.; Zhang, X. M.; Peng, X. M.; Yue, W. J.; Chin. J. Chem. Eng. 2008, 16, 881. [Bmim][CF3SO3],3333 Eßer, J.; Wasserscheid, P.; Jess, A.; Green Chem. 2004, 6, 316. [Omim][OcSO4],3333 Eßer, J.; Wasserscheid, P.; Jess, A.; Green Chem. 2004, 6, 316. [Bmim]AlCl4,3434 Bösmann, L.; Datsevich, A.; Jess, A.; Lauter, C.; Schmitz, P.; Wasserscheid, P.; Chem. Commun. 2001, 23, 2494. [Bmim]Cl/Cu2Cl3,3535 Huang, C. P.; Chen, B. H.; Zhang, J.; Liu, Z. C.; Li, Y. X.; Energy Fuels 2004, 18, 1862. [1-ethyl-3-methylimidazolium (Emim)]dicyanamide (DCA)3636 Yu, G.; Li, X.; Liu, X. X.; Asumana, C.; Chen, X.; Ind. Eng. Chem. Res. 2011, 50, 2236. and [Bmim]DCA.3737 Asumana, C.; Yu, G.; Li, X.; Zhao, J. J.; Liu, G.; Chen, X.; Green Chem. 2010, 12, 2030. Compared with EDS alone using ILs, some researchers observed that ODS is much more efficient and S-removal can be increased up to 90% from 10-40% in EDS, such as [butyl-6-methylquinolinium (Bmimquin)]DCA in ODS process removed 99.9% of S-contents at mild conditions from model diesel fuel.3838 Devi Wilfred, C.; Salleh, M. Z. M.; Mutalib, M. I. B.; Sep. Sci. Technol. 2015, 50, 159. In a typical ODS, S-compounds in gasoline fuel are extracted into the IL phase first, then oxidized by some oxidant, and the oxidized product is more polar and easily removable. The oxidant is usually the cheap and environmentally benign hydrogen peroxide (H2O2) solution, while the catalysts are usually acetic acid,3939 Ali, S. H.; Hamad, D. M.; Albusairi, B. H.; Fahim, M. A.; Energy Fuels 2009, 23, 5986. vanadium pentoxide,4040 Xu, D.; Zhu, W. S.; Li, H. M.; Zhang, J. T.; Zou, F.; Shi, H.; Yan, Y. S.; Energy Fuels 2009, 23, 5929. decatungstates,4141 Li, H. M.; Jiang, X.; Zhu, W. S.; Lu, J. D.; Shu, H. M.; Yan, Y. S.; Ind. Eng. Chem. Res. 2009, 48, 9034. peroxotungsten, or peroxomolybdenum complexes.4242 Zhu, W. S.; Li, H. M.; Jiang, X.; Yan, Y. S.; Lu, J. D.; Xia, J. X.; Energy Fuels 2007, 21, 2514.

Due to regeneration and contamination problems of acid catalyst, recently, some acidic ILs have been used in ODS, where those ILs act as both catalyst and solvent, and no other acid catalyst is added, as shown in Figure 2. In the literature, most emphases are placed on model fuel oils, which are configured by S-compounds (thiophene, dibenzothiphene, and their derivatives) and a certain amount of aliphatic (hexane, heptane, n-dodecane, etc.) and aromatic (usually toluene) compounds while the investigations on real feedstock are rather scarce, as listed in Table 1. The results for model oils may not present a conclusive argument.

Figure 2
Oxidation of S-component using H2O2 and ILs.

Table 1
ODS of real fuels by ILs

In this work, we synthesized four Brønsted acidic ILs namely [Hnmp]HSO4, [Hnmp]H2PO4, [Bmim]H2PO4 and [Bmim]HSO4 and investigated the desulfurization of real fluidized catalytic cracking (FCC) gasoline in two steps: the first in ODS using above ILs as extractant and catalyst and H2O2 as oxidant; the second in EDS using different organic solvents of furfural, furfural alcohol and ethylene glycol (the ILs, also organic solvents, used in this work are illustrated in Figure 3), involving a variety of factors such as temperature, time, and regeneration of ILs, multiple-step desulfurization and solvent/oil mass ratio. These ILs act as both catalyst and solvent, also can easily be prepared with cheaper starting materials and can be regenerated easily, whereas all selected organic solvents are also reasonable candidates for EDS due to their physical characteristics, i.e., immiscible with gasoline (gasoline is miscible with most organic solvents), low volatility, less operational problems, good thermal stability and high boiling points (160-200 ºC). This work shows that ODS using ILs coupled with EDS using organic solvents is a potential method to produce clean gasoline.

Figure 3
Structures of ILs and organic solvents used in this work.

Experimental

Chemicals and material

The chemicals are: N-methylimidazole (≥ 99.0%) (Shanghai SenHao Fine Chemical); ethyl acetate (≥ 99.0%), H2O2 aqueous solution (30 wt.%), H2SO4 (98%), H2PO4 (85%), N-methylpyrrolidone (NMP), furfural alcohol, furfural and ethylene glycol (Beijing Chemical Plant). N-Methylimidazole is further purified by distillation, and the other chemicals were used as received without further purification. Real FFC gasoline fuel with a total S-content of 260 ppm was supplied by SINOPEC Beijing Yanshan Petrochemical Co., Ltd (properties of gasoline are given in Table 2).

Table 2
Physicochemical properties of gasoline

Synthesis of ILs

[Hnmp]HSO4, [Hnmp]H2PO4, [Bmim]HSO4 and [Bmim]H2PO4 were synthesized according to the procedures as mentioned in the literature.5353 Zhang, C.; Pan, X. Y.; Yu, M. J.; Jin, L.; Wu, G.; Chem. Eng. J. 2012, 209, 464.

54 Tajik, H.; Niknam, K.; Parsa. F.; J. Iran. Chem. Soc. 2009, 6, 159.
-5555 Wang, W.; Shao, L.; Cheng, W.; Yang, J.; He, M.; Catal. Commun. 2008, 9, 337.

Preparation of [Hnmp]HSO4 and [Hnmp]H2PO4

NMP (60 mL) was placed in a three-necked flask, which was provided with a stirrer at room temperature. Then, stoichiometric amount of H2SO4 (98%) or H2PO4 (85%) was added to the three-necked flask slowly over a period of 1 h while stirring at room temperature. The reaction mixture was stirred and heated to 80 ºC for 2 h. The residual reactant and water were removed by a rotary evaporator. The IL was dried in vacuum to give the product as a colorless liquid.

The nature of cation and anion in [Hnmp]HSO4 and [Hnmp]H2PO4 was determined with Fourier transform infrared (FTIR) spectroscopy and nuclear magnetic resonance (NMR) spectra.

[Hnmp]HSO4

IR (KBr) νmax / cm-1 3406.2, 2979.5, 2895.7, 2521.7, 1825.8, 1698.4, 1495.5, 1460.9, 1409.8, 1313.0, 1230.4, 1167.7, 1021.7, 982.6, 881.0, 645.5, 578.4, 465, 434.8; 1H NMR (400 MHz, D2O) δ 4.88 (bs, 1H), 3.24-3.20 (t, 2H), 2.54 (s, 3H), 2.17-2.13 (d, 1H).1.77-1.73 (m, 2H).

[Hnmp]H2PO4

IR (KBr) νmax / cm-1 2940.0, 2891.3, 1627.7, 1509.0, 1408.8, 1307.6, 1260.9, 1117.0, 1003.7, 884.1, 747.8, 665.1, 665.1, 617.7, 486.2, 403; 1H NMR (400 MHz, D2O) δ 4.82 (bs, 1H), 3.32-3.28 (t, 2H), 2.45 (s, 3H), 2.08-2.04 (d, 1H), 1.7-1.67 (m, 2H).

Preparation of [Bmim]HSO4 and [Bmim]H2PO4

[Bmim]HSO4 and [Bmim]H2PO4 derived from imidazole chloride salts were obtained by a drop-wise addition of one equivalent of concentrated H2SO4 (98%) or H2PO4 (85%) to solution of the corresponding 1-butyl-3-methylimidazolium chloride in anhydrous methylene chloride. The reaction proceeded at room temperature for 24 h with vigorous stirring under a stream of dry nitrogen. Then, the mixture was dried in vacuum by a rotary evaporator to remove the HCl and solvent to obtain the viscous clear [Bmim]HSO4 and [Bmim]H2PO4.

Desulfurization and recycling

IL and desired amount of 30 wt.% H2O2 were introduced into a 150 mL round-bottom flask. The FCC gasoline fuel was added, then mixture was magnetically stirred for specified time and temperature for ODS process. Then the mixture was allowed to settle for 5 min to obtain phase splitting and the S-content in the upper oil phase was measured. For EDS using organic solvents, desired amount of organic solvent and FCC gasoline fuel were put into 150 mL round-bottom flask. Then mixture was magnetically stirred at a desired time and temperature. The upper oil phase was periodically removed and analyzed for S-content. After each ODS, the bottom IL phase was treated with a rotary evaporator to remove impurities, and the IL was recycled.

S-content analysis

The S-content in real FFC gasoline fuel oil was analyzed by a WK-2D microcoulomb analyzer (Jiangfen Electroanalysis Co., Ltd.), in which high purity nitrogen gas was used as carrier gas while oxygen gas was used as reaction gas; select vaporization zone temperature: 620 °C; combustion zone temperature: 820 °C; temperature of stable segment: 720 °C.

Results and Discussion

ODS using ILs

The ODS results of FFC gasoline fuel by four Brønsted ILs for one step at 60 ºC, time = 4 h, IL/oil mass ratio = 1 and O/S molar ratio = 16 are shown in Figure 4. Efficiency of S-removal from FFC gasoline follows the order [Hnmp]HSO4 > [Hnmp]H2PO4 > [Bmim]HSO4 > [Bmim]H2PO4 with S-removal efficiencies of 25.3 > 23.8 > 20.9 > 18.2%, respectively. Here, the S-removal efficiency is defined as

Figure 4
ODS S-removal efficiency by four Brønsted acidic ILs: [Hnmp]HSO4, [Hnmp]H2PO4, [Bmim]HSO4, and [Bmim]H2PO4 (after one-step ODS, 60 °C, 4 h, 260 ppm of initial S-content, 16 of molar ratio of O/S, 1:1 of mass ratio of IL/oil).

where S0 is the S-content in the gasoline before ODS and Sf is the S-content after ODS. The acidities of [Hnmp]HSO4 and [Hnmp]H2PO4 are expected to be stronger than that of [Bmim]HSO4 and [Bmim]H2PO4, respectively, because there is acidic proton on [Hnmp]+, which is favorable when ILs act as acidic catalyst. [Hnmp]HSO4 and [Hnmp]H2PO4 with highest desulfurization efficiency are chosen to undergo further investigation for the different parameters on S-removal efficiency such as reaction time, temperature, multiple ODS steps, recycling efficiency.

Reaction time

The ODS results using [Hnmp]HSO4 and [Hnmp]H2PO4 at 2, 4, and 6 h are shown in Figure 5. Four hours are enough to reach the equilibrium of desulfurization when the S-removal efficiencies are 25.4 and 23.7% for [Hnmp]HSO4 and [Hnmp]H2PO4, respectively, at 60 °C, IL/oil = 1 and O/S = 16 after single step, while S-removal are only slightly increased to 25.6 and 24.1%, respectively, after 6 h. Two hours are too short when the S-removal efficiencies are 16.2 and 17.1% for [Hnmp]HSO4 and [Hnmp]H2PO4, respectively. Thus, 4 h may be considered as a moderate time for better ODS desulfurization result.

Figure 5
Influence of time on ODS S-removal efficiency of [Hnmp]H2PO4 and [Hnmp]HSO4 (after one-step ODS, 60 °C, 260 ppm of initial S-content, 16 of molar ratio of O/S, 1:1 of mass ratio of IL/oil).

Reaction temperature

The effects of temperature on ODS desulfurization performance by [Hnmp]HSO4 and [Hnmp]H2PO4 are investigated at 30, 45 and 60 ºC. The results are shown in Figure 6. A rise in the reaction temperature from 30 to 60 ºC leads to a remarkable increase in the S-removal efficiency using [Hnmp]HSO4 and [Hnmp]H2PO4 from 12 to 25.3% and 11.6 to 23.7%, respectively, with one step (4 h, IL/oil = 1, O/S = 16). These results can be explained by the strong dependence of the oxidation reaction rate on the reaction temperature. In addition, higher temperature may decrease the viscosity of ILs, enhance effective mixing and inter-phase mass transfer, and H2O2 may be used effectively after decomposition.5050 Nie, Y.; Dong, Y. X.; Bai, L.; Dong, H. F.; Zhang, X. P.; Fuel 2013, 103, 997.

51 Zhao, D. S.; Wang, Y. N.; Duan, E. H.; Molecules 2009, 14, 4351.
-5252 Chen, X.; Guo, H.; Abdeltawab, A. A.; Guan, Y.; Al-Deyab, S. S.; Yu, G.; Yu, L.; Energy Fuels 2015, 29, 2998. On the other hand, too high temperatures are not good choice and might lead to auxiliary risk of explosion in the process, although high temperature enhances H2O2 decomposition. Therefore, reaction at higher temperature should be carefully avoided. Thus, a moderate temperature of 60 °C presents the best desulfurization result.

Figure 6
Influence of temperature for ODS S-removal efficiency of [Hnmp]H2PO4 and [Hnmp]HSO4 (after one-step ODS, 4 h, 260 ppm of initial S-content, 16 of molar ratio of O/S, 1:1 of mass ratio of IL/oil).

IL regeneration

Regeneration of ILs is a necessary process from environmental and economical point of view. After each ODS run, the ILs phase undergoes rotary evaporation to remove impurities, and then the system is charged again with fresh H2O2 solution for the next ODS cycle. The desulfurization results by [Hnmp]HSO4 and [Hnmp]H2PO4 after six cycles are shown in Figure 7. Results indicate that [Hnmp]HSO4 and [Hnmp]H2PO4 can be regenerated and then recycled more than six times with no notable decline in efficiency, e.g., the S-removal only drops from 25.2 to 23.7% for [Hnmp]HSO4 and 23.8 to 22.4% for [Hnmp]H2PO4. This small decline might be ascribed to accumulation of oxidation products.5252 Chen, X.; Guo, H.; Abdeltawab, A. A.; Guan, Y.; Al-Deyab, S. S.; Yu, G.; Yu, L.; Energy Fuels 2015, 29, 2998.

Figure 7
Influence of IL recycling on S-removal efficiency by [Hnmp]HSO4 and [Hnmp]H2PO4 (after one-step ODS, 60 °C, 4 h, 260 ppm of initial S-content, 16 of molar ratio of O/S, 1:1 of mass ratio of IL/oil).

Multiple-step ODS

ODS by multiple-step is an effective way to reduce the S-content of heterocyclic compounds in FCC gasoline. The desulfurization results after multiple-step are shown in Figure 8. After first ODS step, S-content from real FCC gasoline decreased from 260 to 194.6 ppm by [Hnmp]HSO4, and to 198 ppm by [Hnmp]H2PO4 with 25.3 and 23.8% desulfurization efficiencies. After six ODS cycles, desulfurization efficiencies of real FFC gasoline fuel by [Hnmp]HSO4 and [Hnmp]H2PO4 increased to 57 and 62%, respectively. Overall, this performance is not at desired level, when we compare these results with ODS using ILs of model fuels from literature due to complex composition of real FCC gasoline.

Figure 8
Influence of multiple steps of ODS desulfurization of [Hnmp]HSO4 and [Hnmp]H2PO4 (60 °C, 4 h, 260 ppm of initial S-content, 16 of molar ratio of O/S, 1:1 of mass ratio of IL/oil).

EDS using organic solvent after ODS

The EDS results by furfural, ethylene glycol and furfural alcohol for gasolines A and B are shown in Figure 9, where gasoline A is the gasoline after one-step ODS by [Hnmp]HSO4 and gasoline B is that after one-step ODS by [Hnmp]H2PO4. As shown in Figure 9, these solvents present very different EDS capability. It is observed interestingly that the final S-contents in gasoline can be reduced to < 20 ppm with about 95% S-removal after 5-step EDS by furfural and furfural alcohol; while the EDS capability by ethylene glycol is far from that by furfural and furfural alcohol, e.g., the final S-content in gasoline is larger than 110 ppm with only about 55% S-removal by ethylene glycol. As shown in Table 1, where some ODS results of real gasoline and diesel fuel using ILs are summarized, our results are very competitive. It has to be mentioned that the ODS results for gasoline are not as good as diesel fuel, which might be ascribed to the different S-species in gasoline and diesel fuel. Further, Figure 9 shows furfural alcohol has slightly better ODS capacity than furfural, and furfural alcohol can reduce the S-content in gasoline A to 16.1 ppm (93% S-removal) and in gasoline B to 16.8 ppm (94% S-removal). Furfural alcohol was chosen to undergo further investigation for the extraction temperature, extraction time, and solvent/gasoline ratio for gasolines A and B.

Figure 9
EDS S-removal efficiency of (a) gasoline A and (b) gasoline B by organic solvents (40 °C, 1 h, 1:1 of mass ratio of solvent/oil).

Extraction temperature

The results of one-step EDS by furfural alcohol for gasolines A and B at 30, 40, 50 and 60 ºC are shown in Figure 10. The best results are obtained at 40 ºC, where the S-contents are reduced to 144 and 142 ppm for gasolines A and B, respectively (1 h, mass ratio of solvent/oil 1:1). The S-removals at 30 ºC are slightly lower than that at 40 ºC, which might be ascribed to the slow mass transfer at lower temperature. As a whole, the temperature has limited impact on desulfurization in the investigated temperature range.

Figure 10
Influence of temperature for EDS S-removal efficiency for gasolines A and B (after one-step EDS, 1 h, 1:1 of mass ratio of solvent/oil).

Extraction time

The results of one-step EDS by furfural alcohol for gasolines A and B at 15, 30, 60 and 120 min are shown in Figure 11. As shown in Figure 11, the extractive equilibrium can be reached after 30 min, when the S-contents are decreased to 143 and 145 ppm for gasolines A and B, respectively.

Figure 11
Influence of time for EDS S-removal efficiency for gasolines A and B (after one-step EDS, 40 °C, 1:1 of mass ratio of solvent/oil).

Solvent/oil ratio

The solvent/oil mass ratio is one of the important factors for the selectivity of solvent for desulfurization. The results of one-step EDS by furfural alcohol for gasolines A and B at the solvent/oil mass ratios of 3:1, 2:1, 1:1 and 1:2 are shown in Figure 12. As expected, more S-removal is observed with more furfural alcohol, i.e., a larger solvent/oil mass ratio. We have to carefully select the solvent/oil mass ratio and compare between the S-removal efficiency and the solvent cost in industry.

Figure 12
Influence of solvent/oil ratio for EDS S-removal efficiency for gasolines A and B (after one-step EDS, 40 °C, 1 h).

Conclusions

ODS by ILs, as an alternative method to HDS, has been intensively studied recently. In this work, we synthesized four Brønsted acidic ILs of [Hnmp]HSO4, [Hnmp]H2PO4, [Bmim]H2PO4 and [Bmim]HSO4 that are easily prepared with cheap starting materials, and investigated the desulfurization of real FCC gasoline in two steps, first ODS using these ILs as solvent and catalyst with 30 wt.% H2O2 as oxidant, and second EDS using different organic solvents of furfural, furfural alcohol and ethylene glycol as extractants. The more acidic [Hnmp] ILs with proton have better ODS performance than [Bmim] ILs, following [Hnmp]HSO4 > [Hnmp]H2PO4 > [Bmim]HSO4 > [Bmim]HPO4. The S-content in the FCC gasoline with initial S-content of 260 ppm can be decreased to 194 ppm (25.3% S-removal) by [Hnmp]HSO4 and 198 ppm (23.7% S-removal) by [Hnmp]H2PO4 after one-step ODS (60 °C, IL/oil = 1, O/S = 16), and be further decreased to 111 ppm (57% S-removal) and 99 ppm (62% S-removal), respectively, after six-step ODS at the same conditions. The S-content in gasoline after one-step ODS can be significantly decreased to < 20 ppm by EDS using organic solvents, e.g., the five-step EDS using furfural alcohol as extractant (40 °C, 1 h, mass ratio of solvent/oil 1:1) can reduce the S-content to 16-17 ppm with ca. 94% S-removal. The work shows that ODS using ILs coupled with EDS using organic solvents is a potential method to produce clean gasoline.

Acknowledgments

This work was financially supported by National Natural Science Foundation of China (21176021, 21276020). We extend our appreciation to the Deanship of Scientific Research at King Saud University for funding the work through the research group project No. RG-1436-026.

References

  • 1
    Abdalla, Z. E. A.; Li, B.; Tufail, A.; J. Ind. Eng. Chem. 2009, 15, 780.
  • 2
    Seeberger, A.; Jess, A.; Green Chem 2010, 12, 602.
  • 3
    Abro, R.; Abdeltawab, A. A.; Al-Deyab, S. S.; Yu, G.; Qazi, A. B.; Gao, S.; Chen, X.; RSC Adv 2014, 67, 35302.
  • 4
    Ibrahim, J. J.; Gao, S.; Abdeltawab, A. A.; Al-Deyab, S. S.; Yu, L.; Yu, G.; Chen, X.; Yong, X.; Sep. Sci. Technol 2015, 50, 1166.
  • 5
    http://www.unep.org/transport/pcfv/PDF/Session3-Asia-TanDagang-MEPChina.pdf, accessed in December 2015.
    » http://www.unep.org/transport/pcfv/PDF/Session3-Asia-TanDagang-MEPChina.pdf
  • 6
    Gao, S.; Chen, X.; Abro, R.; Abdeltawab, A. A.; Al-Deyab, S. S.; Yu, G.; Ind. Eng. Chem. Res 2015, 54, 9421.
  • 7
    Hernández-Maldonado, A. J.; Yang, R. T.; Ind. Eng. Chem. Res 2003, 42, 123.
  • 8
    Hernández-Maldonado, A. J.; Yang, F. H.; Qi, G.; Yang R. T.; Appl. Catal., B 2005, 56, 111.
  • 9
    Baeza, P.; Aguila, G.; Gracia, F.; Araya, P.; Catal. Commun 2008, 9, 751.
  • 10
    Jiang, W.; Zhu, W.; Li, H.; Wang, X.; Yin, S.; Chang, Y.; Li, H.; Fuel 2015, 140, 590.
  • 11
    Jiang, W.; Zhu, W.; Chang, Y.; Chao, Y.; Yin, S.; Liu, H.; Zhu, F.; Li, H.; Chem. Eng. J. 2014, 250, 48.
  • 12
    Ko, N. H.; Lee, J. S.; Huh, E. S.; Lee, H.; Jung, K. D.; Kim, H. S.; Cheong, M.; Energy Fuels 2008, 22, 1687.
  • 13
    Zhu, W.; Dai, B.; Wu, P.; Chao, Y.; Xiong, J.; Xun, S.; Li, H.; Li, H.; ACS Sustainable Chem. Eng 2015, 3, 186.
  • 14
    Zhu, W.; Wang, C.; Li, H.; Wu, P.; Xun, S.; Jiang, W.; Chen, Z.; Zhao, Z.; Li, H.; Green Chem 2015, 17, 2464.
  • 15
    Shan, G.; Xing, J.; Zhang, H.; Liu, H.; Appl. Environ. Microbiol 2005, 71, 4497.
  • 16
    Monticello, D. J.; Curr. Opin. Biotechnol. 2000, 11, 540.
  • 17
    Alessandro, N.; Tonucci, L.; Bonetti, M.; Deo, M. D.; Bressan, M.; Morvillo, A.; New J. Chem 2003, 27, 989.
  • 18
    Liu, S. Z.; Wang, B. H.; Cui, B. C.; Sun, L. L.; Fuel 2008, 87, 422.
  • 19
    Schmitz, C.; Datsevitch, L.; Jess. A.; Chem. Eng. Sci. 2004, 59, 2821.
  • 20
    Zannikos, F.; Lois, E.; Stournas. S.; Fuel Process. Technol 1995, 42, 35.
  • 21
    Otsuki, S.; Nonaka, T.; Takashima, N.; Qian, W. H.; Ishihara, A.; Imai, T.; Kabe, T.; Energy Fuels 2000, 14, 1232.
  • 22
    Ramírez-Verduzco, L. F.; Torres-García, E.; Gómez-Quintana, R.; González-Peña, V.; Murrieta-Guevara, F.; Catal. Today 2004, 98, 289.
  • 23
    Campos-Martin, J. M.; Capel-Sanchez, M. C.; Perez-Presas, P.; Fierro, J. L. G.; J. Chem. Technol. Biotechnol 2010, 85, 879.
  • 24
    Sobati, M. A.; Dehkordi, A. M.; Shrahokhi, M.; Fuel Process. Technol 2010, 91, 1386.
  • 25
    Shiraishi, Y.; Tachibana, K.; Hirai, T.; Komasawa, I.; Ind. Eng. Chem. Res. 2002, 41, 4362.
  • 26
    Aquino, A. S.; Bernard, F. L.; Vieira, M. O.; Borges, J. V.; Rojas, M. F.; Vecchia, F. D.; Ligabue, R. A.; Seferin, M.; Menezes, S.; Einloft, S.; J. Braz. Chem. Soc 2014, 25, 2251.
  • 27
    Zhang, M.; Li, M.; Chen, Q.; Zhu, W.; Li, H.; Yin, S.; Li, Y.; Li, H.; RSC Adv 2015, 93, 76048.
  • 28
    de Souza, M. O.; J. Braz. Chem. Soc 2014, 25, 2140.
  • 29
    Zhang, S. G.; Zhang, Z. C.; Green Chem. 2002, 4, 376.
  • 30
    Zhang, S. G.; Zhang, Q. L.; Zhang, Z. C.; Ind. Eng. Chem. Res. 2004, 43, 614.
  • 31
    10. Alonso, L.; Arce, A.; Francisco, M.; Soto, A.; J. Chem. Thermodyn. 2008, 40, 966.
  • 32
    Chu, X. M.; Hu, Y. F.; Li, J. G.; Liang, Q. Q.; Liu, Y. S.; Zhang, X. M.; Peng, X. M.; Yue, W. J.; Chin. J. Chem. Eng. 2008, 16, 881.
  • 33
    Eßer, J.; Wasserscheid, P.; Jess, A.; Green Chem. 2004, 6, 316.
  • 34
    Bösmann, L.; Datsevich, A.; Jess, A.; Lauter, C.; Schmitz, P.; Wasserscheid, P.; Chem. Commun 2001, 23, 2494.
  • 35
    Huang, C. P.; Chen, B. H.; Zhang, J.; Liu, Z. C.; Li, Y. X.; Energy Fuels 2004, 18, 1862.
  • 36
    Yu, G.; Li, X.; Liu, X. X.; Asumana, C.; Chen, X.; Ind. Eng. Chem. Res. 2011, 50, 2236.
  • 37
    Asumana, C.; Yu, G.; Li, X.; Zhao, J. J.; Liu, G.; Chen, X.; Green Chem 2010, 12, 2030.
  • 38
    Devi Wilfred, C.; Salleh, M. Z. M.; Mutalib, M. I. B.; Sep. Sci. Technol 2015, 50, 159.
  • 39
    Ali, S. H.; Hamad, D. M.; Albusairi, B. H.; Fahim, M. A.; Energy Fuels 2009, 23, 5986.
  • 40
    Xu, D.; Zhu, W. S.; Li, H. M.; Zhang, J. T.; Zou, F.; Shi, H.; Yan, Y. S.; Energy Fuels 2009, 23, 5929.
  • 41
    Li, H. M.; Jiang, X.; Zhu, W. S.; Lu, J. D.; Shu, H. M.; Yan, Y. S.; Ind. Eng. Chem. Res 2009, 48, 9034.
  • 42
    Zhu, W. S.; Li, H. M.; Jiang, X.; Yan, Y. S.; Lu, J. D.; Xia, J. X.; Energy Fuels 2007, 21, 2514.
  • 43
    Lo, W. H.; Yang, H. Y.; Wei, G. T.; Green Chem. 2003, 5, 639.
  • 44
    Li, F. T.; Kou, C. G.; Sun, Z. M.; Hao, Y. J.; Liu, R. H.; Zhao, D. S.; J. Hazard. Mater. 2012, 205, 164.
  • 45
    Chen, X. C.; Song, D. D.; Asumana, C.; Yu, G. R.; J. Mol. Catal. A: Chem 2012, 359, 8.
  • 46
    Lu, L.; Cheng, S. F.; Gao, J. B.; Gao, G. H.; He, M. Y.; Energy Fuels 2007, 21, 383.
  • 47
    Zhao, D. S.; Sun, Z. M.; Li, F. T.; Shan, H. D.; J. Fuel Chem. Technol. 2009, 37, 194.
  • 48
    Gao, H. S.; Guo, C.; Xing, J. M.; Zhao, J. M.; Liu, H. Z.; Green Chem 2010, 12, 1220.
  • 49
    Yu, G.; Zhao, J.; Song, D.; Asumana, C.; Zhang, X.; Chen, X.; Ind. Eng. Chem. Res. 2011, 50, 11690.
  • 50
    Nie, Y.; Dong, Y. X.; Bai, L.; Dong, H. F.; Zhang, X. P.; Fuel 2013, 103, 997.
  • 51
    Zhao, D. S.; Wang, Y. N.; Duan, E. H.; Molecules 2009, 14, 4351.
  • 52
    Chen, X.; Guo, H.; Abdeltawab, A. A.; Guan, Y.; Al-Deyab, S. S.; Yu, G.; Yu, L.; Energy Fuels 2015, 29, 2998.
  • 53
    Zhang, C.; Pan, X. Y.; Yu, M. J.; Jin, L.; Wu, G.; Chem. Eng. J. 2012, 209, 464.
  • 54
    Tajik, H.; Niknam, K.; Parsa. F.; J. Iran. Chem. Soc. 2009, 6, 159.
  • 55
    Wang, W.; Shao, L.; Cheng, W.; Yang, J.; He, M.; Catal. Commun. 2008, 9, 337.

Publication Dates

  • Publication in this collection
    June 2016

History

  • Received
    12 Aug 2015
  • Accepted
    16 Dec 2015
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