Rashid Abro
a,
Masroor Abroa,
Shurong Gaoa,
Abdul Waheed Bhutto
b,
Zeenat M. Alic,
Asif Shahd,
Xiaochun Chen
*a and
Guangren Yu
*a
aBeijing Key Laboratory of Membrane Science & Technology, College of Chemical Engineering, Beijing University of Chemical Technology, Beijing 100029, P. R. China. E-mail: gryu@mail.buct.edu.cn; chenxc@mail.buct.edu.cn; Fax: +86-10-6443-4892; Tel: +86-10-6443-4892
bDepartment of Chemical Engineering, Dawood University of Engineering and Technology, Karachi, Pakistan
cDepartment of Chemical Engineering, Mehran University of Engineering and Technology, Jamshoro, Pakistan
dKey Laboratory of Materials Modification by Laser, Ion, and Electron Beams (Ministry of Education), School of Materials Science and Engineering, Dalian University of Technology, Liaoning, 116024, P. R. China
First published on 23rd September 2016
Elimination of nitrogen (N) compounds contained in fuel oils is one of the essential processes for petroleum refinery due of their hindering consequences on the hydrodesulfurization (HDS) process. Traditional hydrodenitrogenation (HDN) techniques have some barriers to produce lower-N or N-free fuel oils, e.g., HDN is less effective to remove some cyclic N-compounds; HDN is expensive because of operating conditions such as high pressure and high temperature, and also requires the presence of an expensive catalyst and hydrogen. Application of ionic liquids (ILs) for the purpose of fuel oil extractive denitrogenation (EDN) has been an important part of research in recent years, and it has shown huge potential as an effective substitute or supplemental technique to HDN. In the present review, we studied research results of EDN using ILs and have discussed widely the diversified factors influencing denitrogenation. This review concludes that EDN employing ILs has a promising future owing to the ideal physical and chemical characteristics of ILs; though for such a new technology there are some challenges, for which a discussion is also given. This review contributes proposals for possible commercial application of ILs in EDN.
In consideration of this, other methods such as extraction denitrogenation (EDN), oxidation denitrogenation (ODN), adsorptive denitrogenation (ADN) and biodenitrogenation (BDN), are currently under study.11–18 Among these, EDN is a desirable method because it only needs moderate operating conditions and maintains the structures of compounds in fuel oils. Previously, a few molecular solvents such as pyrimidinone, polyalkylene glycol, imidazolidinone, dimethyl sulfoxide and polyethylene glycol were analysed in EDN; however, the volatile behaviour of these solvents, combined with the small number of suitable extractants, prevented their utilization in industry owing the cost of loss of volatile solvent and difficulty in regeneration.
Ionic liquids (ILs) are also a candidate for EDN. ILs differ from traditional molecular compounds as they contain organic cations and organic/inorganic anions; as a result ILs have an insignificant vapour pressure. Moreover, most ILs have negligible or zero volatility (and thus ILs are considered as “green solvents”). In addition, ILs are highly stable both thermally as well as chemically, with a fabulous capability to dissolve and extract organic or inorganic compounds, they show a widespread liquidus range, are non-flammable and are easily recyclable. All these features favour ILs as solvents in EDN. Fig. 1 illustrates the flow diagram of general EDN using ILs, where extraction of N-compounds from the oil phase to the IL phase is conducted in the first stage and then either simple distillation is carried out for their removal from the IL phase (IL regeneration), taking advantage of the fact that ILs are non-volatile, or an alternative solvent is used for re-extraction employing adjustable solubility between the IL and the solvent.19–24
In recent years, EDN using ILs has been studied intensively. The research observations show good prospects for EDN using ILs as a substitute or supplemental method to HDN though some problems still occur. Several review articles have been published concerning denitrogenation of fuel oils,25–28 for example, Martinez-Palou et al.25 wrote a review article, concerning the applications of ILs for the removal of all types of pollutants including N-compounds from refinery feedstocks. Khan et al.26 summarized the already existing literature on the adsorptive removal of various hazardous compounds including N-compounds from fuel oils in his review paper using air by pristine or modified MOF materials. However, no review articles have focussed on EDN using ILs in detail. In this review paper, we have presented the research results of EDN using ILs and give wide-ranging discussions on a variety of factors for EDN, such as nature of ILs, cross solubility of ILs and oils, time, temperature, mass ratio of ILs and fuel oils, initial N-content, multiple extraction and regeneration. This review can be regarded as significant because of its possible contribution to not only experimental work on EDN using ILs but also on possible commercial application.
IL/organic solvent | Oil | T/°C | IL:oil | N-Rem. (%) | Ref. |
---|---|---|---|---|---|
[Bmim]BF4 | Model diesel oil | RT | 1:1 | 60.0 | 30 |
[Bmim]OcSO4 | Model diesel oil | RT | 1:1 | 41.2 | 31 |
[Emim]EtSO4 | Model diesel oil | RT | 1:1 | 54.5 | 31 |
[Bmim]Cl | Straight-run diesel feed (carbazole) | 60 | 1:10 | 48.0 | 32 |
[OPy]Cl | Straight-run diesel feed (carbazole) | 60 | 1:10 | 58.0 | 32 |
[Bmim]BF4 | Model oil (pyridine in n-C12) | RT | 1:2 | 45 | 32 |
[Emim]N(CN2) | Model oil (pyridine in n-hexane) | 25 | 1:1 | 69.1 | 29 |
[EtMe2S]N(CN2) | Model oil (pyridine in n-hexane) | 25 | 1:1 | 59.8 | 29 |
[S2]N(CN2) | Model oil (pyridine in n-hexane) | 25 | 1:1 | 63.5 | 29 |
[Bmim]N(CN2) | Model oil (pyridine in n-hexane) | 25 | 1:1 | 72.7 | 29 |
DMSO | Pyridine | 25 | 1:1 | 98.6 | 33 |
Carbazole | 25 | 1:1 | 79.9 | ||
DMF | Pyridine | 25 | 1:1 | 96.4 | 33 |
Carbazole | 25 | 1:1 | 81.8 | ||
Acetic acid | Pyridine | 25 | 1:1 | 62.8 | 33 |
Carbazole | 25 | 1:1 | 100 |
Property | Description |
---|---|
Composition | Cation and/or anion quite large |
Melting point | Preferably <100 °C |
Liquidus range | Usually >200 °C |
Thermal stability | Usually high |
Chemical stability | Usually high |
Viscosity | High, <100 cP workable in liquid–liquid extraction |
Dielectric constant | Implied <30 |
Polarity | High to moderate |
Specific conductivity | Usually <10 mS cm−1 |
Molar conductivity | <10 S cm2 mol−1 |
Electrochemical window | >2 V |
Solvent and/or catalyst | Excellent for many organic reactions |
Vapor pressure | Often negligible |
Fig. 3 shows common cation families of ILs while common anions include Cl/[AlCl3]−, N(CN2)−, Br−, Cl−, I−, NO3−, SO4−, CF3COO−, CF3SO2−, BF4−, PF6−, HSO4−, H2PO4− and CF3(SO2)2N−. In recent years, a number of publications have appeared which provide the results of EDN using ILs;29,30,30,32,42–51 ILs used in EDN are listed in Table 4.
IL | Formula | Ref. |
---|---|---|
1-Butyl-3-methylimidazolium dicyanamide | [Bmim]N(CN)2 | 29 |
1-Ethyl-3-methylimidazolium dicyanamide | [Emim]N(CN)2 | 29 |
Ethylated tetrahydrothiophenium dicyanamide | [S2]N(CN)2 | 29 |
Ethyldimethylsulfonium dicyanamide | [EtMe2S]N(CN)2 | 29 |
1-Butyl-3-methylimidazolium chloride | [Bmim]Cl | 32 |
1-Octylpyridinium chloride | [OcPy]Cl | 32 |
1-Butyl-3-methylimidazolium tetrafluoroborate | [Bmim]BF4 | 30 |
1-Butyl-3-methylimidazolium octyl sulfate | [Bmim]OcSO4 | 31 |
1-Ethyl-3-methylimidazolium ethyl sulfate | [Emim]EtSO4 | 31 |
1-Butyl-3-methylimidazolium chloride/ZnCl2 | [Bmim]Cl/ZnCl2 | 42 |
1-Butyl-3-methylimidazolium hydrogen sulfate | [Bmim]HSO4 | 42 |
1-Hexyl-3-methylimidazolium hydrogen sulfate | [Hmim]HSO4 | 42 |
1-Ethyl-3-methylimidazolium tetrafluoroborate | [Emim]BF4 | 30 |
1-Ethyl-3-methylimidazolium ethyl sulfate | [Emim]EtSO4 | 43 |
1-Pentyl-3-methylimidazolium bis(trifluoromethylsulfonyl)imide | [Pmim]Tf2N | 43 |
1-Hexyl-3,5-dimethylpyridinium bis(trifluoromethylsulfonyl)imide | [HmmPy]Tf2N | 43 |
1-Benzyl-3-methylimidazolium bis(trifluoromethylsulfonyl)imide | [Bzmim]Tf2N | 43 |
1-Heptyl-2,3-dimethylimidazolium bis(trifluoromethylsulfonyl)imide | [Hpmmim]Tf2N | 43 |
1-Decyl-2,3-dimethylimidazolium bis(trifluoromethylsulfonyl)imide | [Ocmmim]Tf2N | 43 |
3-Methyl-N-butylpyridinium dicyanamide | [3-mebupy]N(CN)2 | 44 |
4-Methyl-N-butylpyridinium dicyanamide | [4-mebupy]N(CN)2 | 44 |
4-Methyl-N-butylpyridinium trithiocyanate | [4-mebupy]C(CN)3 | 44 |
1-Ethyl-3-methylimidazolium ethyl sulfate–zinc chloride | [Emim]ZnCl2(EtSO4) | 45 |
1-Butyl-3-methylimidazoliumtrifluoromethanesulfonate | [Bmim]OTf | 46 |
1-Ethyl-3-methylimidazole acetate | [Emim]OAc | 47 |
1-Ethyl-3-methylimidazolium ethyl sulfate | [Emim]EtSO4 | 47 |
1-Ethyl-3-methylimidazolium methanesulfonate | [Emim]MeSO4 | 47 |
1-Butyl-3-methylimidazolium tricyanomethanide | [Bmim]TCM | 48 |
1-Butyl-1-methylmorpholinium tricyanomethanide | [Bmomr]TCM | 48 |
1-Butyl-1-methylpyridinium tricyanomethanide | [Bmpy]TCM | 48 |
N-Butylmethylimidazolium dihydrogen phosphate | [Bmim]H2PO4 | 49 |
1-Methyl-3-(3-sulfopropyl)imidazolium dihydrogen phosphate | [Mimps]H2PO4 | 49 |
1-Ethyl-3-methylimidazolium ethyl sulfate | [Emim]EtSO4 | 50 |
1-Ethyl-3-methylpyridinium ethyl sulfate | [Empy]EtSO4 | 50 |
1-Ethyl-3,5-dimethyl-2-pentylpyridinium bis(trifluoromethylsulfonyl)imide | [1B3M5M2PPy]NTf2 | 51 |
1-Butyl-3,5-dimethyl-2-pentylpyridinium dicyanamide | [1B3M5M2PPy]N(CN)2 | 51 |
EDN efficiency of low viscous cyanamide-based ILs with imidazolium, thiophenium, tetrahedral trialkylsulfonium and pyridinium cations was also investigated by Asumana et al. and Hansmeier et al. Both results supported the fact that ILs show high capability to purify fuel oils from N-compounds. Moreover, carbazole was extracted with more efficiency in comparison to pyridine. This extraction capability of imidazolium and pyridinium ILs was better than for other cation based ILs.
Bronsted acid ILs have also been reported for EDN. Chen et al.42 and Wang et al.49 investigated the EDN efficiency of Bronsted acid ILs [Bmim]Cl/ZnCl2, [Bmim]Cl/2ZnCl2, [Bmim]HSO4, [Hmim]HSO4, [Bmim]H2PO4 and [Mimps]H2PO4 using pyridine, neutral carbazole and quinoline as representative N-compounds. It was determined that these ILs have high capability to remove the N-compounds from fuel oils. Typically, using [Bmim]Cl/ZnCl2 in extraction (temperature: 25 °C; 1:1 (w/w) IL:oil), 93.8% of carbazole and 98% pyridine removal was recorded after only a single stage extraction and the N-contents were become indiscernible after two-stage extraction, while ILs ([Bmim]H2PO4, and [Mimps]H2PO4) were also found to be efficient for quinolone extraction. Experimental results thus show the acidity of ILs also contributes to their EDN efficiency.42,49
Vilas et al.51 measured the liquid–liquid equilibrium (LLE) data for ternary mixtures of heptane, nitrogen compound and IL at a temperature of 298.15 K and atmospheric pressure. The variation of selectivity (S) and solute distribution ratio (β) vs. aromatic compound content in the IL-rich phase is plotted in Fig. 4, which shows an increase in aromatic content leads to decreasing S and β values. Here, β is defined as the ratio of solute concentration in the extract phase to that of in the raffinate phase as given in eqn (1) and S is defined as the ratio of solute distribution coefficient to the distribution coefficient of hydrocarbon (HC) as given in eqn (2).
(1) |
(2) |
Fig. 4 Selectivity, S, and solute distribution ratio, β, as a function of the aromatic compound mole fraction in the IL-rich phase, for the ternary systems: (○) {heptane (1) + thiophene (2) + [1B3M5M2PPy][NTf2] (3); (●) {heptane (1) + pyrrole (2) + [1B3M5M2PPy][NTf2] (3)}; (■) {heptane (1) + pyrrole (2) + [1B3M5M2PPy][N(CN)2] (3)} and (□) {heptane (1) + pyridine (2) + [1B3M5M2PPy][N(CN)2] (3)} at T = 298.15 K.51 |
Fig. 4 shows that the {heptane (1) + pyrrole (2) + [1B3M5M2PPy][N(CN)2] (3)} system achieved highest S and β values.51 The corresponding triangular diagram is shown in Fig. 5. As expected, heptane is less soluble than pyrrole in the studied ILs, which could be attributable to π–π interactions between pyrrole and the aromatic core of the IL cations.
Fig. 5 Experimental tie-lines for the LLE for the ternary mixture {heptane (1) + pyrrole (2) + [1B3M5M2PPy][DCN] (3)} at T = 298.15 K.51 |
According to the experimental studies by Domanska and Lukoshko, equilibrium compositions of the experimental tie-line ends in three ternary systems {IL (1) + pyridine (2) + heptane (3)} at T = 298.15 K and ambient pressure revealed almost the absence of IL in the raffinate (heptane) layer after LLE experiment which suggest that “entrainer lost” should not be expected.48 Absence of ILs in the raffinate phase is favourable for industrial applications because fewer steps, and ultimately less energy, is required to recover the solvent for recycling.52
The order of the extraction applicability given by Domańska and Lukoshko is: [Bmmor]TCM (S and β are in range 5.9–609.3 and 1.38–9.20, respectively) > [Bmpy]TCM (S and β are in range of 10.7–578.8 and 1.46–9.42, respectively) > [Bmim]TCM (S and β are in range of 30.3–540.3 and 2.47–11.30, respectively).48
In the non-random two-liquid (NRTL) model, the non-randomness of the mixture is measured by the non-randomness parameter (αij). The mixture is considered to be an ideal solution (i.e. completely random) when the value of αij is zero. LLE data for ternary systems of different ILs with different nitrogen compounds and model fuels were determined both experimentally and by the NRTL model by Domanska et al. with [Bmim]OTf and [Omim]NTf2 and tricyanomethanide-based ILs of [Bmim], [Bmmor] and [Bmpy] cations. It was observed that all these ILs have good capacity for denitrogenation. They enable full denitrogenation from fuel oils in three/four extraction steps with low amount of IL.
Ceron et al.53 synthesized 56 ILs in parallel under microwave irradiation and they were evaluated as extracting agents for N-containing compounds from a real fuel feed before being subjected to HDS to acquire zero-sulfur oil. Halogenated ILs are found as an excellent alternative since these ILs are relatively inexpensive, affirming a high selectivity for the extraction of N-containing compounds with positive regeneration and recycling ability.
Chen et al.42 investigated EDN efficiency of acidic ILs for basic (i.e., pyridine) and non-basic (i.e., carbazole) N-compounds. An interesting result was found: whereas for the basic pyridine, EDN efficiency is 97%, for the non-basic carbazole, the efficiency is variable: 93.2, 90.1, 71.2 and 24.2% for [Bmim]Cl/ZnCl2, [Bmim]HSO4, [Bmim]Cl/2ZnCl2 and [Hmim]HSO4, respectively; such different extractive capabilities for the non-basic compound might be ascribed to their different anionic nature and length of alkyl side chain on the cation.42
Ramalingam et al.54 predicted the energetic and structural characteristics of the complexes between [EMIM]EtSO4 and various N-compounds by application of quantum chemical calculations. [EMIM]EtSO4 IL can be easily synthesized, recovered and regenerated under the prescribed conditions by dilution with water followed by distillation ([EMIM]EtSO4: molecular weight; 236 g, flash point; 162 °C, density; 1.24 g mL−1, refraction index; 1.481, melting point; <−30 °C, polar surface area; 8.81 Å). In that study an ab initio method was used for the determination of the interaction energies, structure, partial charges of atom in the molecules, highest occupied molecular orbital (HOMO) energy, lowest unoccupied molecular orbital (LUMO), chemical potential, chemical hardness and softness, electronegativity and electrophilicity index of Emim, EtSO4 and [Emim]EtSO4 interacting with pyrrole, quinoline, benzoquinoline, pyrrole, indole, indoline, carbazole and benzocarbazole. During the formation of interactive bonds between similar and dissimilar molecules their structure is of central importance. Charges in arrangement in the surrounding of molecules is found to be influential towards the absorption capacity. Both HOMO and LUMO energy play an important role in the interaction between low-reactivity N-molecules and [EMIM]EtSO4. For effective interaction between [EMIM]EtSO4 and N-molecules, orbital level interaction has been proved to be among the main parameters. Electronegativity, chemical hardness, chemical potential and electrophilicity index of all N-compounds also influence their behavior and interaction will depend on ease of polarization of both electron donors and acceptors. After the separation process, the easy recovery and regeneration of [Emim]EtSO4 under the supposed conditions has been indicated by the low chemical softness of individual molecules as compared to the complexes. Based on that, [Emim]EtSO4 IL is regarded as a potential solvent to separate all types of N-compounds contained in diesel oil under normal conditions. Xie et al.,55 in their study, focused upon the possible significance of hydrogen bond basicity of chloride-based ILs to achieve the separation of compounds with a hydrogen-donor group (i.e. neutral N-compounds) existing in hydrocarbon feeds with a high selectivity towards basic N-compounds and sulfur-containing compounds.
Hizaddin et al.52 performed chemical calculations using ab initio quantum methods to determine the optimized geometry of individual cations, anions, heterocyclic N-compounds, complexes of ILs, and complexes of heterocyclic N-compounds with eighteen ILs. The interaction between ILs and heterocyclic N-compounds due to CH–π and π–π bonding between the cations and N-heterocycles and hydrogen bonding between anion heteroatoms and heterocyclic N-compounds has been verified by their optimized structure with ILs. Calculation of partial charge transfer, global scalar properties, orbital energy values and interaction energy has been done for each individual species as well as in the complexes. According to the obtained results ILs are identified as being suitable for the denitrification of fuel oils by extraction. The obtained results strongly suggest all of the eighteen ILs mentioned in present work as potential solvents for denitrification of fuel oils due to favorable interactions as indicated by orbital energies, global scalar properties, interaction energy, partial charge transfer and sigma profiles. Although, some ILs undergo effective interaction with heterocyclic N-compounds on the basis of each parameter investigated, each parameter also serves to rank ILs on the basis of favorable interaction with N-compounds. Based on LUMO energy values, HOMO–LUMO gap, global softness and electrophilicity index, [Epy]EtSO4 is the most favorable IL for heterocyclic N-compound extraction. However, on the basis of interaction energy and partial charge transfer, [TMPYRA][Ac] is a more preferable IL. The σ-profile and σ-potential of each cation, anion and N-heterocycle confirm mutual interaction among the three species. Based on σ-profile and σ-potential, ILs with aromatic ring cations ([Emim], [Epy] and [TMPYRA]) have better capacity in donating hydrogen bonds as compared to saturated cations, thus, enabling better CH–π interaction with heterocyclic N-compounds.
Fig. 6 Time for the extractive removal of carbazole from fuel oils using high viscous ILs.42 |
Fig. 7 Effect of time on N-removal efficiency (quinolone). Conditions: IL/oil = 1:10, IL/H2O: 2:1, T = 25 °C, settlement time = 30 min.49 |
Fig. 8 Time for the extractive removal of carbazole from fuel oils using low viscous ILs.29 |
Fig. 9 Time for the extractive removal of pyridine fuel oils using low viscous ILs.29 |
(3) |
Dearden et al.56 examined the factors that can affect the measurement of partition coefficients. It was reported that the accuracy of partition coefficient determination can be affected by temperature, lack of mutual phase saturation, pH, buffer type and concentration, phase miscibility, solute concentration, solute solvent purity, solute stability, phase volume ratio, solute adsorption and failure to reach equilibrium conditions.
Overall it is found from the literature of EDN using ILs, that the N-Nernst partition coefficient is not too sensitive to the mass ratio of IL:oil in EDN under different conditions. This kind of inertness is helpful for industrial application because high N-removal can then be possible with smaller IL:oil ratio (i.e., economizes on ILs). Fig. 10 and 11 depict the N-Nernst partition coefficient of [Bmim]N(CN)229 and oil at different initial N-contents and temperatures, respectively.
Fig. 10 N-Extraction efficiency and KN-Nernst partition coefficient by [Bmim]N(CN)2 for pyridine-containing fuel oil at different initial N-contents.29 |
Fig. 11 N-Extraction efficiency and KN-Nernst partition coefficient by [Bmim]N(CN)2 for pyridine-containing fuel oil at different extraction temperatures.29 |
IL | N-Compound | N-Extraction efficiency for IL–oil mass ratio | Conditions | Ref. | ||||
---|---|---|---|---|---|---|---|---|
2:1 | 1:1 | 1:2 | 1:3 | 1:5 | ||||
a INC is initial N-content. | ||||||||
[Bmim]Cl/ZnCl2 | Pyridine | 98 | 98 | 97 | 97 | 97 | INC: 483 ppm, fuel oil: 1:1 (w/w) IL:oil; t: 20 min, T: 298 K | 42 |
[Bmim]Cl/ZnCl2 | Carbazole | 98 | 93 | 86 | 81 | 71 | INC: 279 ppm, fuel oil: 1:1 (w/w) IL:oil; t: 20 min, T: 298 K | 42 |
[Bmim]N(CN)2 | Pyridine | 83 | 72.1 | 57 | 46 | 36 | INC: 483 ppm, fuel oil: 1:1 (w/w) IL:oil; t: 20 min, T: 298 K | 29 |
[Bmim]N(CN)2 | Carbazole | n/a | n/a | 95 | 92 | 87 | INC: 258 ppm, fuel oil: 1:1 (w/w) IL:oil; t: 20 min, T: 298 K | 29 |
[Pmim]Tf2N | Pyridine | n/a | 70 | 57 | n/a | ∼40 | Fuel oil: 1:1 (w/w) IL:oil; t: 20 min, T: 298 K | 43 |
[HmmPy]Tf2N | Pyridine | n/a | 68 | 51 | n/a | 39 | Fuel oil: 1:1 (w/w) IL:oil; t: 20 min, T: 298 K | 43 |
In addition to the positive effect of enhancing IL/oil mass ratio, it has to be selected with care on the basis of a compromise between N-removal and fuel oil recapture. Furthermore the capacity to regenerate ILs must also be taken into consideration since it vastly contributes the total cost of process.
IL | N-Compound | Time/min | N-Extraction efficiency for temperatures (%) | Ref. | ||||
---|---|---|---|---|---|---|---|---|
20 °C | 25 °C | 35 °C | 45 °C | 55 °C | ||||
[Bmim]/Cl/ZnCl2 | Pyridine | 20 | 98 | 98 | 97.2 | 96 | 95.5 | 42 |
Carbazole | 20 | 95 | 94 | 93.8 | 93.3 | 91 | 42 | |
[Emim]N(CN)2 | Pyridine | 20 | 72 | 71.2 | 70.4 | 69.5 | 68.9 | 29 |
[Bmim]H2PO4 | Quinoline | 20 | 99 | 99.6 | 99.6 | 99.7 | 98.3 | 49 |
[Mimps]H2PO4 | Quinoline | 20 | 99 | 99.6 | 99.7 | 99.7 | 98.4 | 49 |
IL | Oil | N-Compound | Initial N-content | IL–oil mass ratio | Time/min | N-Extraction efficiency for multiple steps (%) | Ref. | |||
---|---|---|---|---|---|---|---|---|---|---|
1 | 2 | 3 | 4 | |||||||
[Bmim]N(CN)2 | Diesel | Pyridine | 479 | 1:1 | 20 | 74 | 42.1 | 96.8 | n/a | 29 |
[Emim]EtSO4 | Gasoline | Pyridine | n/a | 1:4 | 20 | 27.5 | 49.1 | 70.5 | 70.5 | 29 |
Diesel | Pyridine | n/a | 1:4 | 20 | 30.2 | 45.4 | 66.1 | 86.2 | ||
[Pmim]Tf2N | Gasoline | Pyridine | n/a | 1:4 | 20 | 45.6 | 58.6 | 70.2 | 78.6 | 43 |
Diesel | Pyridine | n/a | 1:4 | 20 | 35.1 | 49.6 | 76.9 | 87.8 | 43 | |
[HmmPy]Tf2N | Gasoline | Pyridine | n/a | 1:4 | 20 | 39.2 | 45.8 | 65.7 | 75.7 | 43 |
Diesel | Pyridine | n/a | 1:4 | 20 | 7.43 | 58.7 | 71.6 | 98.9 | 43 | |
[BZmim]Tf2N | Gasoline | Pyridine | n/a | 1:4 | 20 | 36.2 | 54.7 | 68.4 | 70.2 | 43 |
Diesel | Pyridine | n/a | 1:4 | 20 | 42.8 | 62.6 | 72.6 | 80.6 | 43 | |
[HPmmim]Tf2N | Gasoline | Pyridine | n/a | 1:4 | 20 | 32.1 | 53.3 | 67.6 | 70.6 | 43 |
Diesel | Pyridine | n/a | 1:4 | 20 | 41.1 | 65.5 | 78.7 | 81.0 | 43 | |
[Dmmim]Tf2N | Gasoline | Pyridine | n/a | 1:4 | 20 | 32.5 | 54.3 | 67 | 77.1 | 43 |
Diesel | Pyridine | n/a | 1:4 | 20 | 38.9 | 60.4 | 74.0 | 81.5 | 43 | |
[Bmim]Cl/ZnCl2 | Pyridine | n/a | 1:1 | 30 | 99 | n/a | n/a | n/a | 42 | |
Carbazole | 279 | 1:1 | 30 | 87.5 | n/a | n/a | n/a | 42 |
Fig. 12 N-Extraction efficiency vs. regeneration cycle of [Bmim][N(CN)2] for carbazole- and pyridine-containing fuel oils (temperature: 25 °C; mass ratio of IL:oil = 1:1; extraction time: 20 min).29 |
Fig. 13 N-Extraction efficiency vs. regeneration cycle of [Bmim]H2PO4 and [Mimps]H2PO4 for quinolone – containing fuel oils (temperature: 25 °C; mass ratio of IL:oil = 1:10; extraction time: 30 min).49 |
As shown in Fig. 12, [BMI]N(CN)2; after five cycles, 100% N-extraction efficiency for carbazole-containing fuel oil is maintained, while for pyridine, N-extraction efficiency is slightly reduced from 72 to 70%.29 Similar trends were observed for other studies of EDN using ILs. Therefore ILs have proven to be not only good extractants but also good candidates for industrial application.
Many researchers have investigated ILs efficiency for extractions of impurities from fuel oils, but few had addressed this important issue that could circumvent the applicability of certain ILs. Overall, it is simply presumed that ILs do not dissolve into fuel oils due to their ionic and high polar nature. However, some researchers observed a degree of solubility of ILs with fuel oils, as shown in Table 8. Jiang et al. calculated model gasoline solubility in ILs, [Mmim]DMP 1.1%, [Emim]DEP 4.2% and [Bmim]DBP 20.6 wt%, at 298 K. Also, solubility values of gasoline, 2.06 wt% in [Emim]DMP, 5.81 in [Emim]DEP, 26.69 in [Beim]DBP, 3.53 in [Bmim]DMP and 10.2 in [Beim]DEP were obtained. While analyzing solubility of model oil in [Bmim]N(CN)2 and [Emim]N(CN)2, it was observed to be insignificantly soluble at a low content of toluene but it was found to raise by increasing the concentration of toluene in model oil (e.g., for [Bmim]N(CN)2, 6.7 wt% for 20% mass fraction of toluene; for [Emim]N(CN)2, 3.08 wt% for 15% mass fraction of toluene). Hansmeier et al. observed that the solubility of [Bmpy]BF4 and [Emim]EtSO4 in n-heptane was 0.3 and 0.9 mol%, respectively. The study of solubility of various ILs with different organic compounds has also been carried out. Most ILs have a degree of solubility in a few organic compounds such as acetone, ethanol, methanol and water, but much less so in hexane, toluene or heptane. The literature regarding cross solubility of liquid fuels and ILs suggests that cross solubility of ILs with fuel oils has to be given more attention in studies to optimize various future applications.
IL | Fuel | Oil solubility in IL (wt% or ppm) | IL solubility in oil (wt%) | Ref. |
---|---|---|---|---|
[Mmp]DMP | n-Octane | 1.17 | 0.04 | 57 |
[Mep]DEP | n-Octane | 5.83 | 0.14 | 57 |
[Hmp]DMP | n-Octane | 0.46 | n/a | 57 |
[Hmp]DMP | n-Octane | 4.56 | 0.09 | 57 |
[Emim]DMP | Gasoline | 20.6 | n/a | 58 |
[Emim]DEP | Gasoline | 5.81 | n/a | 58 |
[Beim]DBP | Gasoline | 26.9 | n/a | 58 |
[Mmim]DMP | Gasoline | 11.2 | n/a | 58 |
[Emim]DEP | Gasoline | 42.5 | n/a | 58 |
[Bmim]DBP | Gasoline | 20.6 | n/a | 58 |
[Emim]DEP | Gasoline | 2.25 | n/a | 59 |
[Bmim]DBP | Gasoline | 20.6 | n/a | 59 |
[Mmim]DMP | Gasoline | 1.12 | n/a | 60 |
[Emim]DEP | Diesel | 4.25 | n/a | 60 |
[Bmim]DBP | Diesel | 20.6 | n/a | 60 |
[Bmim]DMP | Diesel | 35.5 | n/a | 61 |
[Bpy]BF4 | Model oil | 0.49 | n/a | 62 |
[Opy]BF4 | Diesel | 1.97 | n/a | 62 |
[Bmim]/Cl | Diesel | 25 ppm | n/a | 32 |
[Almim]Cl | Diesel | 25 ppm | n/a | 32 |
[Bzmim]Cl | Diesel | 35 ppm | n/a | 32 |
[Ocmim]Cl | Diesel | 370 ppm | n/a | 32 |
[OcPy]Cl | Diesel | 15 ppm | n/a | 32 |
[Bmim]OCSO4 | n-Dodecane | 4.0 | n/a | 31 |
1-Octane | 22 | n/a | 31 | |
[Emim]ETSO4 | n-Dodecane | 1 | n/a | 31 |
1-Octane | 2.8 | n/a | 31 | |
[Bmim]N(CN)2 | Gasoline | 6.66 | n/a | 29 |
Diesel | 1.97 | n/a | 29 | |
[Emim]N(CN)2 | Gasoline | 5.64 | n/a | 29 |
Diesel | 1.93 | n/a | 29 | |
Et3NNHCl3·FeCl3 | Model oil | 0.27 | n/a | 63 |
Real gasoline | 2.45 | n/a | ||
[Bmpy]BF4 | n-Dodecane | 6.1 | n/a | 64 |
[Hmpy]BF4 | n-Dodecane | 7.6 | n/a | 64 |
[Ompy]BF4 | n-Dodecane | 9.5 | n/a | 64 |
[Bmin]DCNM | n-Hexane | 4.19 | n/a | 65 |
In contemporary studies, the N-extraction efficiency is not ideal for ILs. Generally 3–5 re-extraction steps with high oil–ILs mass ratios are required to lower the N-content to <10 ppm. Keeping in view the fact of ILs are more expensive than other organic solvents, a variety of factors need to be considered during their selection such as chemical/thermal stability, cross solubility with fuel oils, and ease of regeneration. Consequently further attention is required to be focused towards rationally designing task-specific ILs especially for producing environment friendly fuel oils.
Previous literature suggests some ILs are not truly green solvents66,67 and doubts in their sustainable development impede their applications as real green solvents. Wide-ranging research concerning the behavior of ILs is still required to be done. The significant features which should be considered to acquire an in-depth perception into environmental consequences of ILs are as given below. (1) A basic understanding into the mechanism for IL-induced toxicity at different levels of complexity as the underlying mechanisms of IL toxicity have rarely been studied. (2) Investigating the biodegradability of cationic and anionic compartments and toxicity of their degradation intermediates. This may provide useful information for designing safe and efficient ILs. (3) Developing the database of environmentally benign structure moieties of ILs on the basis of toxicological and biodegradation information, which would be practically useful as a reference for manufacturers and regulators to properly develop and regulate the use of ILs.
In the literature, mostly model oils are analysed with different ILs, which is compulsory for initial assessment. More real fuel oils are required to be studied because besides N-species studied in model fuel oils, there are various additional N-species that may impede the EDN process. This will be essential when shifting from laboratory scale work to pilot plant production.
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