Wenshuai
Zhu
,
Jingtong
Zhang
,
Huaming
Li
*,
Yanhong
Chao
,
Wei
Jiang
,
Sheng
Yin
and
Hui
Liu
College of Chemistry and Chemical Engineering, Jiangsu University, 301 Xuefu Road, Zhenjiang, 212013, P. R. China. E-mail: lihm@ujs.edu.cn; Fax: 86-0511-88791708; Tel: 86-0511-88791800
First published on 16th November 2011
The extraction desulfurization (EDS) and extraction combined with oxidation desulfurization (EODS) for the removal of dibenzothiophene (DBT), benzothiophene (BT), and 4,6-dimethyldibenzothiphene (4,6-DMDBT) in a model oil were carried out in Fenton-like ionic liquids, such as [Et3NHCl]FeCl3, [Et3NHCl]CuCl2, [Et3NHCl]ZnCl2, [Et3NHCl]CoCl2, [Et3NHCl]SnCl2 and [Et3NHCl]CrCl3. The deep desulfurization could be achieved in [Et3NHCl]FeCl3 for only 5 min at room temperature. The reaction conditions such as temperature, the molar ratio of H2O2 and DBT and the amount of ionic liquid (IL) were investigated in the EODS system. By controlling the way of adding H2O2 into the desulfurization system, the sulfur content in the model oil could decrease from 500 mg L−1 to less than 10 mg L−1 at the IL/oil volume of 1
:
5. The oxidation reactivity of the different sulfur-containing compounds was found to be in the order of DBT > BT > 4,6-DMDBT. Moreover, the EODS system could be recycled ten times with a slight decrease in activity to model oil. EODS process was applied to prehydrotreated gasoline and the sulfur content could decrease from 150 to 15 mg L−1 after two rounds of reaction.
In the past several years, nonhydrogenation desulfurization methods, such as the processes of oxidation7–15 and extraction16–21 have been explored. Among these processes, oxidative desulfurization (ODS) has attracted wide interest owing to its advantages like mild conditions, high efficiency and selectivity.3 The ODS process was usually achieved through two steps. Firstly, organic sulfides were selectively oxidized to sulfoxides and sulfones, which further needed to be removed by appropriate extractants or adsorbents.22–24 Recently, oxidative desulfurization with hydrogen peroxide combined with extraction has been considered as one of the most promising processes. DBT and its derivatives can be oxidized to their corresponding sulfoxides and sulfones easily in the ODS process, and can be removed by extraction with organic solvents.3,22 However, the volatile organic compounds employed as extractants result in further environmental concerns.
Ionic liquids (ILs) have received great attention as a new kind of “green solvent”.25–27 The new process for sulfur removal through extraction desulfurization with ILs has been reported in the literature. Many types of ILs have been employed in extraction desulfurization. However, the desulfurization efficiency is relatively low caused by the similar polarity between the sulfur-containing molecules and remaining diesel fuels. As a result, the method of the one-pot chemical oxidation combined with ionic liquids extraction has been developed,28–33 which could improve the desulfurization efficiency effectively. Recently, a liquid–liquid extraction and catalytic oxidative desulfurization (ECODS) system composed of a catalyst, H2O2 and ionic liquid ([bmim]BF4) has been found to be suitable for the deep removal of refractory sulfur compound DBT in a model oil by our group.34–39 The S-removal could achieve deep desulfurization, which was the remarkable advantage of this process over the desulfurization by sole solvent extraction with IL. However, in this ECODS system a higher temperature was required while the reaction time was longer. Besides that, ionic liquids are rather expensive and only act as extractants in the ECODS system.
The iron-based ionic liquids have been employed in many organic reactions, however most attention was paid to the character of the Lewis acid.40–41 Up to now, few studies on its oxidation–reduction character were reported, especially using a Fenton-like agent with H2O2 in oxidative desulfurization. Our group found that a Fenton-like ionic liquid [(n-C8H17)3NCH3]FeCl4 could act as a phase-transfer catalyst in oxidative desulfurization and exhibited high catalytic activity.42 However, this ionic liquid is expensive and the solubility in model oil is relatively big. In this work, inexpensive [Et3NHCl]FeCl3 was synthesized from low cost raw materials and showed good desulfurization efficiency using H2O2 in a one-pot extraction combined with oxidation desulfurization (EODS) system. The solubility of [Et3NHCl]FeCl3 in a model oil was improved greatly. Deep desulfurization could be achieved in [Et3NHCl]FeCl3/H2O2 at room temperature in a very short time (5 min). The ionic liquid acted not only as the catalyst but also as an extractant in the process of desulfurization.
[Et3NHCl]FeCl3, [Et3NHCl]CuCl2, [Et3NHCl]ZnCl2, [Et3NHCl]CoCl2, [Et3NHCl]SnCl2 and [Et3NHCl]CrCl3 were synthesized as mentioned in the literature procedure.41,43 The structure has been identified by IR and Raman and the results were listed in the ESI,† Fig. S2.
![]() | (2) |
The system was applied to the oxidation of prehydrotreated gasoline (150 mg L−1 S, Jiangsu Jia Yu Xin Industrial Co., Ltd.) under optimal conditions. The total sulfur content in prehydrotreated gasoline was analyzed by microcoulometric analyzer (WK-2D, Jiangsu Jiangfen Electroanalytical Instrument Co., Ltd. China, detection limit: 0.5 ppm).
:
10; flowrate, 1.0 mL min−1).
:
5. The results in two different desulfurization systems, including EDS and EODS systems are shown in Fig. 1. As can be seen, compared with [Et3NHCl]FeCl3, [Et3NHCl]CuCl2, [Et3NHCl]ZnCl2, [Et3NHCl]CoCl2, [Et3NHCl]SnCl2 and [Et3NHCl]CrCl3 ionic liquids, the ability for both EDS and EODS of [Et3NHCl]FeCl3 was better. The sulfur removal of DBT in the model oil could only get to 56.8% in the extraction desulfurization system with [Et3NHCl]FeCl3. With the addition of H2O2, the desulfurization efficiency increased greatly, reaching 97.1%. However, the sulfur removal in the desulfurization systems containing other ILs with the same cation was all below 45%. The experimental results indicate that the type of anion in ILs is critical for the removal of DBT in the model oil. As a result, iron-based IL show the highest desulfurization activity among all of the listed ILs.
![]() | ||
| Fig. 1 Comparison of different ionic liquids in EDS and EODS systems. Experimental conditions: EDS: T = 30 °C, t = 10 min, model oil = 5 mL, IL = 2 mL; EODS: T = 30 °C, t = 5 min, model oil = 5 mL, IL = 2 mL, [n(H2O2)/n(DBT) = 6]. | ||
The oxidative desulfurization agreed with the mechanism of extraction combined with oxidation desulfurization.35Sulfur compounds were extracted into IL firstly, and then were oxidized by a oxidizing agent. DBT was firstly oxidized to sulfoxide, and then to sulfone. The remanent sulfur in the model oil was non-oxidated sulfur compounds, which could be testified by gas chromatography-flame ionization detector (GC-FID). Oxidated S-compounds could not be detected by GC-FID in oil phase. To the S-compounds in the IL phase, tetrachloromethane (CCl4) was used to re-extract S-compounds from the IL phase, and then the resulting CCl4 solution was analyzed by GC-FID. The results indicated that DBT, DBTO and DBTO2 co-existed in the IL phase. This phenomena lay in the very short reaction time (only 5 min). During such a short time, DBT was extracted into the IL, but the oxidation was not finished completely. So DBT, DBTO and DBTO2 co-existed in the IL. These results could further validate the mechanism of EODS.
:
1, reaching 97.1% sulfur removal (Table 1, entry 3). When the molar ratio of Et3NHCl to FeCl3 was 1
:
0.5 and 1
:
1.5, sulfur removal was 71.6% and 64.6%, respectively. As described previously, the performance of [Et3NHCl]FeCl3 in the EDS and EDOS systems was excellent, so [Et3NHCl]FeCl3 was the ideal ionic liquid among the studied in this work.
| Entry | IL | Sulfur removal (%) | |
|---|---|---|---|
| EDS b | EODSc | ||
| a Experimental conditions: T = 30 °C, model oil = 5 mL, IL = 2 mL. b t = 10 min. c t = 5 min, [n(H2O2)/n(DBT) = 6]. d m(Et3NHCl) = 1.2451 g. e Results from Li and coworkers.44 | |||
| 1 | Et3NHCl | — | 2.8d |
| 2 | Et3NHCl/0.5FeCl3 | 50.2 | 71.6 |
| 3 | Et3NHCl/FeCl3 | 56.8 | 97.1 |
| 4 | Et3NHCl/1.5FeCl3 | 54.6 | 64.6 |
| 5 | Anhydrous FeCl3 | — | 57.4e |
:
1, 3
:
1, 4
:
1, 5
:
1, 6
:
1, 7
:
1 and 8
:
1 were plotted. The hydrogen peroxide had more opportunity to oxidize DBT and the desulfurization increased as the amount of oxidizing agent increased. The sulfur removal increased from 77.1% (O/S = 2
:
1) to 97.1% (O/S = 6
:
1) at 30 °C for 5 min. When the O/S molar ratio reached 7
:
1 and 8
:
1, the sulfur removal of DBT increased slowly to 97.7% and 98.3%, respectively. It can be also found that the trend of sulfur removal was similar at 40 °C and 50 °C. Therefore, the optimal O/S molar ratio was 6
:
1, owing to the waste of using an excess amount of oxidant.
![]() | ||
| Fig. 2 Influence of H2O2/DBT molar ratio and temperature on sulfur removal of DBT. Experimental conditions: t = 5 min, model oil = 5 mL, IL = 2 mL. | ||
:
10 to 1
:
1 in Fig. 3. The results show that the amount of [Et3NHCl]FeCl3 was a significant parameter influencing the desulfurization efficiency. The sulfur removal of DBT increased with the increase volume ratio of IL and model oil, no matter what desulfurization systems were, such as EDS or EODS. When the volume ratio of IL and model oil was 1
:
10 and 1
:
5, the sulfur removal was bad in both of the two desulfurization systems. As the volume ratio of IL and model oil increased from 2
:
5 to 1
:
1, the sulfur removal of DBT increased slightly from 97.1% to 99.5%. However, the utilization of IL at the IL/oil volume ratio of 1
:
1 would result in wasting resources. Therefore, the most appropriate IL/oil volume ratio was 2
:
5.
![]() | ||
| Fig. 3 Influence of the different contents of IL on sulfur removal of DBT. Experimental conditions: EDS: T = 30 °C, t = 10 min, model oil = 5 mL; EODS: T = 30 °C, t = 5 min, model oil = 5 mL, [n(H2O2)/n(DBT) = 6]. | ||
To achieve the aim of reducing the dosage of [Et3NHCl]FeCl3, a series of experiments through adding H2O2 in batches were designed and the results are shown in Table 2. The gross amounts of H2O2 was the same with the above experiments, and the O/S molar ratio was 6
:
1. Under the reaction conditions of 30 °C for 10 min, 3.0 equivalent H2O2 with DBT was added into the desulfurization system at the time of 0 min and 5 min in turn, respectively. From the data in Table 2, the sulfur removal could reach 98.3% in the given experiment, when the IL/oil volume ratio decreased to 1
:
5 (Table 2, entry 2). As a result, the cheap and low dosage of IL was better for deep desulfurization.
| Entry | V(IL)/V(oil) | Sulfur removal (%) |
|---|---|---|
| a Experimental conditions: T = 30 °C, t = 10 min, model oil = 5 mL, n(H2O2)/n(DBT) = 6, 3.0 equivalent H2O2 with DBT was added into the desulfurization system at the time of 0 min and 5 min in turn, respectively. | ||
| 1 | 2 : 5 |
99.7 |
| 2 | 1 : 5 |
98.3 |
| 3 | 1 : 10 |
78.2 |
![]() | ||
| Scheme 1 Molecular structure of sulfur-contaning compounds. | ||
| Entry | Substrates | S-removal (%) | K N in mg (S) L (IL)−1/mg (S) L (oil)−1b | Electron densityc | |
|---|---|---|---|---|---|
| EODSa | EDS b | ||||
| a Experimental conditions: T = 30 °C, t = 5 min, model oil = 5 mL, V([Et3NHCl]FeCl3) = 2 mL , [n(H2O2)/n(DBT) = 6]. b Experimental conditions: T = 30 °C, t = 10 min, model oil = 5 mL, V([Et3NHCl]FeCl3) = 2 mL. c Results from Otsuki and coworkers.45 | |||||
| 1 | DBT | 97.1 | 56.8 | 3.29 | 5.758 |
| 2 | BT | 86.9 | 56.9 | 3.30 | 5.739 |
| 3 | 4,6-DMDBT | 82.5 | 37.5 | 1.50 | 5.760 |
The process of the EODS system involved extraction and oxidation in two steps, and substrates were extracted from n-octane before they were oxidized in the IL phase. Therefore, the ability of IL to extract sulfur-containing compounds is an important factor influencing desulfurization efficiency. According to EDS data in Table 3, the Nernst partition coefficients (KN) of DBT, BT and 4,6-DMDBT could be calculated by eqn (1).
| KN = mg (Sulfur) L−1 (IL)/mg (Sulfur) L−1 (oil) | (1) |
For example, removal of DBT, BT and 4,6-DMDBT was 56.8%, 56.9% and 37.5%, respectively, and calculated KN was 3.29, 3.30 and 1.50, respectively. As can be seen by KN, [Et3NHCl]FeCl3 ionic liquid showed a better ability than imidazolium-based IL to extract different sulfur compounds.44 Therefore, the larger KN was, the higher the concentration of sulfur compounds in the IL. A high concentration of substrates led to a high reaction rate. Owing to this reason, DBT, BT and 4,6-DMDBT could be removed effectively in the desulfurization containing [Et3NHCl]FeCl3.
From the data in Table 3, the desulfurization efficiency of 4,6-DMDBT was the lowest. This phenomenon can be explained in the following two aspects. On one hand, 4,6-DMDBT shows much lower KN in comparison with DBT and BT. On the other hand, there are two methyl groups in phenyl, causing the higher steric hindrance to S-atom, forming obstacle in the catalytic oxidation. As for DBT and BT, although the KN of DBT was close to that of BT, the electron density on the sulfur atom of DBT is higher than that of BT45 which led to the highest oxidative reactivity. Therefore, the oxidation reactivity of the different substrates was in the following order of sulfur removal: DBT > BT > 4,6-DMDBT, which is affected by electron density, steric hindrance and KN synergistically.
![]() | ||
| Fig. 4 Recycle of [Et3NHCl]FeCl3 ionic liquid in desulfurization system. Experimental conditions: T = 30 °C, t = 5 min, model oil = 5 mL, IL = 2 mL, [n(H2O2)/n(DBT) = 6]. | ||
![]() | ||
| Fig. 5 HPLC chromatograms of [Et3NHCl]FeCl3, n-octane and IL-saturated n-octane. aExperimental conditions: T = 30 °C, t = 10 min, n-octane = 5 mL, IL = 2 mL. | ||
Reusability of [Et3NHCl]FeCl3 has been performed with prehydrotreated gasoline. After the first reaction, the reaction system was still a biphasic system, in which the IL phase was the under-layer and oil phase was the upper-layer. Therefore, the oil phase could be separated from the biphasic system easily. Afterwards, the fresh H2O2 and prehydrotreated gasoline were added in regenerated IL (the method refers to the model oil) for the next run. The results indicated that the [Et3NHCl]FeCl3 could be recycled four times at 30 °C and sulfur removal was 79.3%, 80.1%, 79.4% and 78.8%, respectively. We compared the Raman spectra of fresh [Et3NHCl]FeCl3 with regenerated [Et3NHCl]FeCl3(Fig. 6), which indicated no transformation of the anion [FeCl4]− (333 cm−1). These results also indicated nitrogen compounds (Lewis bases) in real fuels could not deactivate the catalyst and reduce its reusability, which may attribute to the ·OH mechanism in Fenton-like ionic liquids/H2O2 system.44
![]() | ||
| Fig. 6 Raman spectra of fresh [Et3NHCl]FeCl3 and recycled regenerated [Et3NHCl]FeCl3. | ||
:
1. The reaction time of EODS system was very short, consuming only 5 min. The temperature, the H2O2 to DBT molar ratio, the amount of IL all played important roles in the desulfurization efficiency. The sulfur removal could reach 98.3% at room temperature, when the IL/oil volume ratio was 1
:
5 and the H2O2 was added into the desulfurization system at the time of 0 min and 5 min in turn for 10 min. The oxidation reactivity of the different substrates was in the following order: DBT > BT > 4,6-DMDBT. Moreover, [Et3NHCl]FeCl3 was hardly miscible with the model oil. The EODS system could be recycled ten times with a slight decrease in sulfur removal. The sulfur content in prehydrotreated gasoline could decrease from 150 to 15 mg L−1 S after two rounds of reaction. This research extended the function of Lewis acidic IL Et3NHCl/FeCl3 and developed a simple method for deep desulfurization of fuels.
Footnote |
| † Electronic Supplementary Information (ESI) available. See DOI: 10.1039/c1ra00163a/ |
| This journal is © The Royal Society of Chemistry 2012 |