Catalysed oxidation of quinoline in model fuel and the selective extraction of quinoline N oxide with imidazoline based ionic liquids Egyptian Journal of Petroleum xxx (2017) xxx–xxx Contents lists av[.]
Trang 1Full Length Article
Catalysed oxidation of quinoline in model fuel and the selective
extraction of quinoline-N-oxide with imidazoline-based ionic liquids
Adeniyi S Ogunlajaa,⇑, Olalekan S Aladeb
a Department of Chemistry, Nelson Mandela Metropolitan University, P.O Box 77000, Port-Elizabeth 6031, South Africa
b
Petroleum and Petrochemical Engineering Laboratory, Department of Chemical Engineering, Obafemi Awolowo University, Ile-Ife, Osun State, Nigeria
a r t i c l e i n f o
Article history:
Received 4 December 2016
Revised 9 February 2017
Accepted 15 February 2017
Available online xxxx
Keywords:
Vanadium(IV) catalyst
Hydrogen peroxide (H 2 O 2 )
Quinoline
Oxidation
Ionic liquids
a b s t r a c t
Synthesised vanadium-coordinated N,N-bis(o-hydroxybenzaldehyde)phenylene diamine catalyst, [VO (sal-HBPD)] and supported catalyst, p[VO(sal-HBPD)] were employed for the oxidation of quinoline The use of [VO(sal-HBPD)] and p[VO(sal-HBPD)] for the oxidation of quinoline, (Quinoline-to-H2O2ratio 1:7) showed oxidation selectivity as quinoline-N-oxide (100%) was recorded as the oxidation product Quinoline-N-oxide was confirmed as the oxidation product through GC–MS Density functional theory (DFT) revealed hydroxylperoxido-species [VOO(sal-HBPD)] (II) as the reactive oxidized oxidovanadium specie responsible for the oxidation Ionic liquids, 3-methylimidazolium chloride and 1-butyl-3-methylimidazolium nitrate extracted 96% and 87% quinoline-N-oxide respectively
Ó 2017 Egyptian Petroleum Research Institute Published by Elsevier B.V This is an open access article
under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/)
1 Introduction
Environmental concerns have resulted in stringent
specifica-tions for petroleum products including fuel oils; and had
necessi-tated the development of processes to upgrade heavy oil to
environmental friendly products[1] The current crude oil
reser-voirs are known to be of heavier and sourer composition, i.e the
produced oils (as well as their products) come with
organo-sulfur,-oxygen and -nitrogen compounds also known as
heteroa-toms[2–4] The Organo-nitrogen and –sulfur compounds in fuels,
are reported to (i) poison refining catalysts, (ii) emit NOx and
SOx to the environment when combusted, hence reacting with
water to form acid rain, (iii) reduce air quality, and (iv) possibly
lead to global warming[5]
The elimination of organosulfur compounds from fuel has been
largely reported, through the use of hydrodesulfurization (HDS)
process while literature reports on denitrogenation processes are
limited Organo-nitrogen compound removal is required to
main-tain NOx emissions below regulatory levels of <1 ppm, as
hydro-denitrogenation (HDN) process that is currently being employed
for the removal of nitrogenated compounds suffer limitations in
achieving the nitrogen content requirement Catalyst deactivation
as well as the reactivity of N-compounds of some nitrogen-containing compounds (quinoline, indoles, carbazoles, benzcar-bazoles, pyridines, pyrrole, azapyridines, aniline, phenantridines and porphyrins) have been identified as important factor affecting HDN processes Oxidative denitrogenation (ODN), a complemen-tary technique to the HDN, involves the oxidation of nitrogen-containing compounds to N-oxides compounds followed by the selective adsorption of the N-oxides[6] Several adsorbents such
as activated carbon, zeolites, silica, nanofibers, ion-exchange resins have been applied for the removal of nitrogen compounds in fuel oil [6–14] However, a great challenge is the development of an effective adsorbent with high surface area and can selectively adsorb nitrogen compounds in fuel An alternative approach is the use of ionic liquids (ILs) which offered better nitrogen com-pound extraction properties[15–17] In the recent years, ILs have attracted rising attention in the petroleum and petrochemical industries due to their versatility and prospective applications in various areas including flow assurance of viscous and bituminous hydrocarbons for improved production and transportation, upgrading and catalytic removal of heteroatoms and coke from the heavy oil, and surface activeness and potential use in the enhanced oil recovery of heavy oil[18–20]
In the present paper, we present the oxidation of a basic nitrogen compounds found in hydro-treated fuel, quinoline, using vanadium-coordinated N,N-bis(o-hydroxybenzaldehyde) phenylene diamine catalyst, [VO(sal-HBPD)] [21] as a catalyst and H2O2 as an oxidant The oxidation progress was monitored http://dx.doi.org/10.1016/j.ejpe.2017.02.004
1110-0621/Ó 2017 Egyptian Petroleum Research Institute Published by Elsevier B.V.
This is an open access article under the CC BY-NC-ND license ( http://creativecommons.org/licenses/by-nc-nd/4.0/ ).
Peer review under responsibility of Egyptian Petroleum Research Institute.
⇑ Corresponding author.
E-mail address: adeniyi.ogunlaja@nmmu.ac.za (A.S Ogunlaja).
Contents lists available atScienceDirect Egyptian Journal of Petroleum
j o u r n a l h o m e p a g e : w w w s c i e n c e d i r e c t c o m
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Trang 22 Experimental
2.1 Materials
Quinoline (98%, Sigma-Aldrich), hydrogen peroxide (30%, H2O2)
and absolute methanol (Merck Chemical) were used as received
2.2 General procedure for synthesis of catalysts
Vanadium-coordinated N,N-bis(o-hydroxybenzaldehyde)
phenylene diamine ligand, [VO(sal-HBPD)] synthesized and fully
characterized by Ogunlaja et al.[21]was also employed for the
oxi-dation of quinoline Both unsupported [VO(sal-HBPD)] and
sup-ported p[VO(sal-HBPD)] catalysts were employed for the studies
2.3 Metal content determination and leaching studies
Vanadium content on p[VO(sal-HBPD)] was determined by
weighing out 0.0025 g into a vial, and 5 mL of TraceSelect HNO3
(69%) was added This mixture was heated at 50°C for 48 h to leach
out the vanadium The acid-leached solution was then diluted with
deionized-distilled water to 100 mL, filtered with 0.45mM filters
and analysed by Atomic Adsorption Spectrometer (AAS)
2.4 Catalytic oxidation procedure
The catalytic oxidation of a known quantity of quinoline
(2.58 mL, 0.02 mol) was carried out using [VO(sal-HBPD)]/p[VO
(sal-HBPD)] (0.000167 mol of vanadium) and H2O2(0.14 mol) as
an oxidant In a 25 mL round bottom flask containing quinoline,
10 mL of methanol was added and the solution was heated at
drawing aliquots from the reactor at fixed time intervals and analyzing using a gas chromatograph GC conditions were Opti-mized to efficiently separate the products from the reactants in the Zebron Phenomenex ZB-5MSi capillary column (30 m 0.25 mm 0.25lm) on the GC-FID/GC–MS Helium was used as carrier gas at a flow rate of 1.63 mL min1with an average velocity
of 30.16 cm.sec1and a pressure of 63.73 kPa The analysis run was started with an oven temperature of 50°C ramping to 250 °C @
15°C min1 The oxidation products were confirmed using an Agilent 7890A gas chromatograph-mass chromatography (GC–MS) fitted with a 30 m 0.25 mm 0.25 mm DB-5 capillary column 2.6 Computational studies
Density functional theory (DFT) using Becke’s three-parameter hybrid exchange functional in combination with the gradient-corrected correlation functional provided by Perdew/Wang 91 (B3PW91) method[22]with LanL2DZ level was employed in deter-mining the electronic properties of [VO(sal-HBPD)] using the Gaus-sian[23]program (calculated at 298 K)
2.7 Ionic liquid synthesis Ionic liquids, butyl-3-methylimidazolium chloride and 1-Butyl-3-methylimidazolium nitrate were synthesized according
to the procedure reported by Ogunlaja et al.[24] For the purpose
of this report, the synthesis of 1-butyl-3-methylimidazolium chloride was achieved by refluxing a mixture of 1-methylimidazole (25 mL, 0.31 mol) and 1-chlorobutane (36 mL, 0.35 mol) in 50 mL of toluene at 110°C under vigorous stirring for 24 h The resulting brown viscous oil was allowed to cool down for approximately
24 h (Scheme 1), decanted, and then washed with acetonitrile
fol-Scheme 1 Synthesis of 1-butyl-3-methylimidazolium chloride and 1-butyl-3-methylimidazolium nitrate.
Please cite this article in press as: A.S Ogunlaja, O.S Alade, Catalysed oxidation of quinoline in model fuel and the selective extraction of quinoline-N-oxide
Trang 3lowed by ethyl acetate.1
H NMR (d, ppm in DMSO): 9.67 (1H, s), 7.99 (2H, d), 4.22 (2H, t), 3.98 (3H, s), 1.69 (2H, m), 1.09 (2H, m),
0.72 (3H, t) 1-Butyl-3-methylimidazolium nitrate:
1-butyl-3-methylimidazolium chloride (0.29 mol) in dichloromethane was
added to a solution of AgNO3(0.32 mol), and the resulting mixture
was stirred for 24 h (Scheme 1) The white suspended precipitate
of AgCl was filtered over Celite The complete replacement of Cl
with NO3 was established by further addition of a concentrated
AgNO3 solution to the ionic liquid until no precipitation of AgCl
Fig 1 (I) An ORTEP view of [VO(sal-HBPD)] with ellipsoids drawn at 50% probability level and (II) molecularly modelled [VO(sal-HBPD)].
Table 1
Some experimental and optimized calculated bond lengths [Å] parameters of [VO(sal-HBPD)] calculated by DFT (B3PW91) methods with LanL2ZD basis set.
Table 2
Some experimental and optimized calculated bond angles [°] parameters of [VO(sal-HBPD)] calculated by DFT (B3PW91) methods with LanL2ZD basis set.
Table 3
UV electronic properties of [VO(sal-HBPD)].
[VO(sal-HBPD)]
k = wavelength; f = oscillator strength.
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Trang 4closely compare with the experimental data.
3.1.2 Electronic properties (UV adsorption analysis) The electronic properties of [VO(sal-HBPD)] were calculated using the TD-DFT approach on the previously optimized ground-state geometry of the complexes The calculations were performed
in gas phase as carried-out in the experimental studies
TD-DFT calculations predict three transitions in the visible region of the vanadium species with varying intensities and ener-gies The electronic transitions of [VO(sal-HBPD)] in gas phase are presented inTable 3 The maximum absorption wavelength corre-sponds to the electronic transition from the HOMO to LUMO The calculated excitation energies (E), oscillator strength (f) and wave-length (k) and spectral assignments are given inTable 3
Wavelength (nm)
0
1
V
O after 5 h
Fig 2 Spectrophotometric titration of [VO(sal-HBPD)] with H 2 O 2 (2 10 2 M) in
MeOH.
E(LUMO) = -6.75659
E(HOMO) = -9.80835 ΔE= 3.05176
E(LUMO) = -6.80067
E(HOMO) = -9.37977 ΔE= 2.57910
E(LUMO) = -6.78326
E(HOMO) = -9.46059 ΔE= 2.67733
Fig 3 The HOMO and LUMO molecular orbital position of the various oxidovanadium species, [VO(sal-HBPD)] (I) and the two proposed hydroxylperoxido species (II and III) [VOO(sal-HBPD)].
Please cite this article in press as: A.S Ogunlaja, O.S Alade, Catalysed oxidation of quinoline in model fuel and the selective extraction of quinoline-N-oxide
Trang 53.2 Oxidation reaction
3.2.1 Electronic properties of oxidized VO(sal-HBPD)
The oxidation reaction progressed steadily on addition of the
oxidant, H2O2, to quinoline in the presence of catalyst
[VO(sal-HBPD)][21]at 70°C (Quinoline-to- H2O2ratio 1:7) UV/Vis studies
showed that intermediate species were formed during the catalytic
oxidation process through the gradual disappearance of the d–d
bands around 401 nm (Fig 2)[21], hence confirming the oxidation
of oxidovanadium(IV) to dioxidovanadium(V) and oxidoperoxido
species The oxidoperoxido species protonates to form the
hydroxyl-peroxidovanadium(V) species responsible for the
oxida-tion reacoxida-tion
3.2.2 HOMO-LUMO band gap analysis Several authors have revealed the protonation of peroxido moiety leading to a significant drop in the activation barrier for oxi-dation[25,26] However, the position of the protonation of
peroxo-VV-complexes may vary within the moiety[26] Herein, we explore the electronic properties of two proposed peroxido species (II and III), which may occur The molecular orbital plays an important role
in the electric and optical properties of [VO(sal-HBPD)] (I) and the two proposed hydroxylperoxido species (II and III) The HOMO rep-resents the ability to donate an electron, LUMO as an electron accep-tor[25] The plots of the HOMO and LUMO orbitals for the various oxidovanadium species, [VO(sal-HBPD)] (I) and the two proposed hydroxylperoxido species (II and III) were modelled in MeOH, and shown inFig 3 From the computation, it is found that the HOMO positions of complexes I, II and III are localized mostly around
Atoms
-0.8 -0.6 -0.4 -0.2 0.0 0.2 0.4 0.6 0.8
1.0
species II species III
Mulliken's plot
Fig 4 The Mulliken atomic charge plot of the proposed hydroxylperoxido species (II and III).
Table 4
Mulliken atomic charges of [VOO(sal-HBPD)] species (II) and (III) using LanL2DZ basis
set.
Atoms Species (II) Species (III) Atoms Species (II) Species (III)
Table 5 Occupancy of natural orbitals (NBOs) and hybrids of [VO(sal-HBPD)] (I) calculated by the DFT level with LanL2DZ.
s(0.00%) p(100.00%)
s(33.19%) p(66.81%)
s(39.74%) p(60.26%)
s(35.21%) p(64.79%)
s(34.28%) p(65.72%)
s(46.95%) p(53.05%)
s(24.67%) p(75.33%)
s(25.09%) p(74.91%)
r*
r*
s(35.48%) p(64.52%)
s(31.76%) p(68.24%)
r*
r*
s(24.96%) p(75.04%)
* Underlined atoms represent the hybridized position.
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Trang 63.2.3 Mulliken atomic charge
The charge distribution on [VOO(sal-HBPD)] species (II and III)
was modelled to determine the possible species responsible for
the oxidation reaction and also to ascertain its influence on
vibra-tion spectra Mulliken net charges calculated at the DFT level with
LanL2DZ atomic basis set in methanol using Gaussian 09[23] The
vanadium atom V(1) attract the positive charge from the oxygen atom O(40) Atoms O(41) and O(42) of specie [VOO(sal-HBPD)] (II) are more negatively charged as compared to specie [VOO(sal-HBPD)] (III) confirming that its ability to donate more electron, hence more reactive
3.2.4 NBO analysis After establishing the reactivity of [VOO(sal-HBPD)] (II) via energy gap studies, NBO analysis was further performed on [VO (sal-HBPD)] (I) and [VOO(sal-HBPD)] (II) at the DFT level with LanL2DZ in order to elucidate the intra molecular re-hybridization and delocalization of electron density within the complexes[24,27] Three classes of NBOs were observed and these include, (i) Lewis-type (randpbonding or lone pair) orbital’s, (ii) valence non-Lewis (acceptors formally unfilled) orbital’s and (iii) Rydberg NBOs, which originate from orbitals outside the atomic valence shell The calculated occupancies of natural orbitals, calcu-lated natural hybrids on atoms are also given inTables 5 and 6 3-Dimensional plot of the atomic orbital occupancies against the various energies of the vanadium atom in [VO(sal-HBPD)] (I) and [VOO(sal-HBPD)] (II) are providedFig 5 Ther(V1-O40) bond is formed from sp4.11hybrid on O40 (which is the mixture of 19.55%
s and 80.45% p atomic orbital’s), thep(V1-O40) observed bond is formed from sp hybrid on O40, which is predominantly p atomic orbital’s But therandr⁄of [VO(sal-HBPD)] (I) and [VOO (sal-HBPD)] (II) are generally hybrid p-character (Tables 5 and 6)
Table 7 presents the perturbation energies of donor-acceptor interactions of some atoms in [VO(sal-HBPD)] (I) and [VOO(sal-HBPD)] (II)
Table 6
Occupancy of natural orbitals (NBOs) and hybrids of [VOO(sal-HBPD)] (II) calculated
by at the DFT level with LanL2DZ.
s(17.44%) p(82.56%)
s(41.96%) p(58.04%)
s(28.35%) p(71.65%)
s(35.33%) p(64.67%)
s(22.03%) p(77.97%)
s(22.70%) p(77.30%)
s(31.19%) p(68.81%)
r*
r*
s(32.59%) p(67.41%)
s(27.25%) p(72.75%)
r*
*
Underlined atoms represent the hybridized position.
-0.5
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
5 10 15 20
-2.5 -2.0 -1.5 -1.0 -0.5 0.0
0.5
upancy
NA O
Energ y
I
-1 0 1 2 3 4
5 10 15 20
-2.5 -2.0 -1.5 -1.0 -0.5 0.0 0.5
upancy
NA O
Energ y
II
NAO 1
20
Fig 5 A 3D plot of natural atomic orbital occupancies against the various energies for [VO(sal-HBPD)] (I) and [VOO(sal-HBPD)] (II).
Please cite this article in press as: A.S Ogunlaja, O.S Alade, Catalysed oxidation of quinoline in model fuel and the selective extraction of quinoline-N-oxide
Trang 7[VO(sal-HBPD)] (I) perturbation energies of the various
donor-acceptor interactions; [N(4) – C(26)] to [V(1) – O(40)] and
[N(3) – C(36)] to [V(1) – O(40)] are 0.68 kJ/mol and 1.31 kJ/mol
respectively The [N(3) – C(36)] to [V(1) – O(40)] interaction gave
high energies, hence providing a stronger stabilization to the
[VO(sal-HBPD)] (I)
[VOO(sal-HBPD)] (II) perturbation energies of the various
donor-acceptor interactions are provided inTable 7 [V(1) – O(2)]
to [V(1) – N(3)], [V(1) – O(2)] to [V(1) – O(40)] and [V(1) – N(3)]
to [V(1) – O(40)] are 14.81 kJ/mol, 15.27 kJ/mol and 20.53 kJ/mol
respectively The [V(1) – N(3)] to [V(1) – O(40)] interaction gave
high energies, hence providing a stronger stabilization to the
[VOO(sal-HBPD)] (II) [VOO(sal-HBPD)] (II) offered relatively higher
energies as compared with [VO(sal-HBPD)] (III), hence making
[VOO(sal-HBPD)] (II) a more reactive intermediate
3.2.5 Quinoline oxidation From the computationally modelled electronic study, the hydroxyl-peroxidovanadium(V) specie [VOO(sal-HBPD)] (II) is responsible for the electron pairing between the nitrogen atom of quinoline and an oxygen atom of the hydroxyl-peroxidovanadium (V) species, hence leading to bond formation and oxidation (Scheme 2)
Further oxidation mechanism was also followed with EPR anal-ysis (Fig 6), hyperfine interaction lines predominately ascribed to
V4+, [VO(sal-HBPD)] disappeared upon the addition of H2O2
(Fig 6B), indicating the oxidation of the V4+ to V5+ Addition of quinoline to this solution resulted in reduction of the metal center
to V4+ species, (Fig 6C) This occurrence indicates that electron
Table 7
Second order perturbation theory analysis of the Fock matrix in NBO basis.
[VO(sal-HBPD)] (I)
[a.u.]
[VOO(sal-HBPD)] (II)
[a.u.]
a
E(2) means energy of hyper conjugative interaction (stabilization energy).
b
Energy difference between donor and acceptor i and j NBO orbitals.
c
F(i; j) is the Fock matrix element between i and j NBO orbitals.
Scheme 2 Simplified catalytic mechanism for the oxidation of quinoline H + from
H 2 O may protonate peroxido to form the hydroxyl-peroxidovanadium(V) species
(1) Here L may refer to donor atom.
A
B
C
D
Field (Guass)
2800 3000 3200 3400 3600 3800 4000
Fig 6 First derivative EPR spectra of [VO(sal-HBPD)] (0.000167 mol) (A) in MeOH; (B) addition of 7 equiv of H 2 O 2 to the solution of (A); (C) addition of quinoline (0.02 mol) to the solution of (B); and (D) solution of (C) after 24 h.
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Trang 8transfer processes to occur between quinoline and the V5+specie
(hydroxyl-peroxidovanadium(V) species) After a 48 h period, the
catalyst recovers (Fig 6D) with an indication of a slight change in
the vanadium co-ordination geometry
The oxidation of quinoline gave rise to quinoline-N-oxide
(100%), with a turnover frequency (TOF) of 997 h1, while the
supported catalyst p[VO(sal-HBPD)] also gave rise to 100%
quinoline-N-oxide The product (quinoline-N-oxide) was isolated
and analyzed by GC-FID (Fig 7) and GC–MS (Fig 8)
3.3 Adsorption studies
3.3.1 Adsorption of quinoline-N-oxide in model fuel using ionic liquids
5 mL of ionic liquid was contacted with 5 mL of
quinoline-N-oxide (200 ppm) in a mixture of toluene and dichloromethane was
stirred for 3 h at 50 rpm, and thereafter it was allowed to stand for
1 h for a better phase separation A total of 96% and 87%
quinoline-N-oxide were removed when1-butyl-3-methylimidazolium
chlo-ride and 1-butyl-3-methylimidazolium nitrate were employed
respectively (Fig 9)
excited states[28] From the 1-butyl-3-methylimidazolium chloride/quinoline-N-oxide adduct (Fig 10), HOMO originated from the chlorine anion
of 1-butyl-3-methylimidazolium chloride ionic liquid as well as the quinoline-N-oxide molecule while the LUMO position arises from the quinoline-N-oxide (Fig 10) This clearly confirmed that
Time (min)
oxidant
Fig 7 GC-FID chromatograms of quinoline oxidation: Quinoline (2.58 mL,
0.02 mol) and [VO(sal-HBPD)] (0.000167 mol of vanadium).
0 1000 2000 3000 4000 5000 6000 7000 8000 9000
m/z >
145.0
117.0
90.0
63.0 39.0 51.0
75.0
Fig 8 GC–MS chromatogram of quinoline-N-oxide.
Ionic liquid phase
Quinoline-N-oxide in
DCM/Toluene phase
Fig 9 1-Butyl-3-methylimidazolium chloride (IL-Cl) and 1-butyl-3-methylimida-zolium nitrate (IL-NO 3 ) and quinoline-N-oxide.
Please cite this article in press as: A.S Ogunlaja, O.S Alade, Catalysed oxidation of quinoline in model fuel and the selective extraction of quinoline-N-oxide
Trang 9interaction between 1-butyl-3-methylimidazolium chloride and
quinoline-N-oxide through electron transfer took place With
1-butyl-3-methylimidazolium nitrate/quinoline-N-oxide adduct,
both the HOMO and LUMO center emanates from the
quinoline-N-oxide of the ionic liquid (Fig 11)
4 Conclusions
The use of [VO(sal-HBPD)] and p[VO(sal-HBPD)] for the
oxida-tion of quinoline, presented oxidaoxida-tion selectivity as
quinoline-N-oxide (100%) was recorded as the oxidation product UV studies
of [VO(sal-HBPD)] confirmed the formation of
species, DFT electronic studies also confirmed
hydroxylperoxido-species (II) as the reactive oxidized oxidovanadium specie
responsible for the oxidation Ionic liquids,
1-butyl-3-methylimidazolium chloride and 1-butyl-3-1-butyl-3-methylimidazolium
nitrate extracted 96% and 87% quinoline-N-oxide respectively
Acknowledgements
We are thankful for financial support provided by THRIP (SA)
and Sasol (Pty) Ltd as the industrial partner The authors thank
the Center for High Performance Computing (CHPC), Cape Town,
South Africa for providing the platform in carrying out the
molec-ular modelling studies on the Gaussian09 software We would also
like to acknowledge Prof Zenixole R Tshentu (Department of
Chemistry, Nelson Mandela Metropolitan University) for the
research advice as well as providing chemicals employed for the
research study
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Fig 11 (A) HOMO and (B) LUMO positions of 1-butyl-3-methylimidazolium nitrate/quinoline-N-oxide adduct.
Fig 10 (A) HOMO and (B) LUMO positions of 1-butyl-3-methylimidazolium chloride/quinoline-N-oxide adduct.
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Please cite this article in press as: A.S Ogunlaja, O.S Alade, Catalysed oxidation of quinoline in model fuel and the selective extraction of quinoline-N-oxide