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Advances of Ionic Liquids in Analytical Chemistry Maria Jose Trujillo-Rodríguez, He Nan, Marcelino Varona, Miranda Emaus, Israel D Souza, and Jared L. Anderson Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/acs.analchem.8b04710 • Publication Date (Web): 17 Oct 2018 Downloaded from http://pubs.acs.org on October 18, 2018
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Analytical Chemistry
1
Advances of Ionic Liquids in Analytical Chemistry
2 3
María J. Trujillo-Rodríguez,1 He Nan,1 Marcelino Varona,1 Miranda N. Emaus,1
4
Israel D. Souza,1 Jared L. Anderson*,1
5
1Department
of Chemistry, Iowa State University, Ames, Iowa 50011 USA
6 7 8
*Corresponding author at: Department of Chemistry, Iowa State University, 1605 Gilman
9
Hall, Ames, IA, 50011, USA.
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E-mail:
[email protected] 1 ACS Paragon Plus Environment
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Introduction
13
Sample preparation
14
Solid-phase (micro)extraction
15
Ionic liquids and polymeric ionic liquids in solid-phase extraction
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Ionic liquids and polymeric ionic liquids in solid-phase microextraction
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Liquid-phase (micro)extraction
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Ionic liquids and magnetic ionic liquids in dispersive liquid-liquid
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microextraction
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Ionic liquid dispersive liquid-liquid microextraction
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Magnetic ionic liquid dispersive liquid-liquid microextraction
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Ionic liquids and magnetic ionic liquids in single-drop microextraction
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Ionic liquids in hollow fiber liquid-phase microextraction
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Two phase ionic liquid-hollow fiber liquid-phase microextraction
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Three phase ionic liquid-hollow fiber liquid-phase microextraction
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Ionic liquids and magnetic ionic liquids in aqueous biphasic systems Chromatographic and electrophoretic separations Gas chromatography
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Monocationic ionic liquid-based stationary phases
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Di- and polycationic ionic liquid-based stationary phases
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Polymeric ionic liquid-based stationary phases
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Metal-containing ionic liquid-based stationary phases
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Commercial ionic liquid-based stationary phases
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High Performance Liquid Chromatography Ionic liquids as mobile phase additives 2 ACS Paragon Plus Environment
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Analytical Chemistry
Ionic liquids as components of the stationary phase
36 37
Counter-current chromatography
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Capillary electrophoresis
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Mass spectrometry
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Ionic liquids as matrixes in matrix-assisted laser desorption ionization
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Ionic liquids as additives in electrospray ionization mass spectrometry
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Electrochemical sensing systems
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Ionic liquids as electrolyte media
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Ionic liquids/carbon-based composite electrochemical sensing systems
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Ionic liquid/metal-based composite electrochemical sensing systems
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Ionic liquid/hybrid carbonaceous-metal-based composite electrochemical sensing
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systems
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Biosensors based on ionic liquids
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Conclusions and perspectives
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Author information
51
Corresponding author
52
Notes
53
Biographies
54
References
55
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Introduction
57
Ionic liquids (ILs) are a highly unique class of non-molecular solvents that possess melting
58
points below 100 ºC.1 ILs that have melting points below room temperature are often referred
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to as room temperature ionic liquids (RTILs). ILs possess a wide variety of unique physico-
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chemical properties, including low or negligible vapor pressure at room temperature, high
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thermal and electrochemical stability, and high conductivity.2
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ILs are composed completely of ions and are typically asymmetric organic cations containing
63
nitrogen or phosphorous heteroatoms as well as both inorganic and organic anions. Figure 1
64
shows a representative series of typical IL cations and anions. Due to the large diversity of
65
cations and anions, it has been estimated that more than 1018 possible combinations of cations
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and anions can be created.2 It is often the case that small modifications to the cation/anion
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chemical structure or cation/anion combination are accompanied by dramatic modifications
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to their physical properties, including viscosity and water solubility. At the same time, the
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incorporation of polar or non-polar moieties to the IL structure can promote different
70
interactions with solutes and impressive solvation capabilities for different classes of
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compounds. For all of these reasons, ILs are normally referred to as designer solvents.
72
Since the introduction of ILs, several subclasses of ILs have been popularized and studied
73
within the analytical sciences, including task-specific ILs (TSILs), chiral ILs, polymeric ionic
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liquids (PILs) and magnetic ionic liquids (MILs). TSILs are ILs with functional groups that
75
impart specific properties or reactivity to the IL.3 PILs are polymeric materials generated
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through the polymerization of IL monomers.4,5 In comparison to ILs, PILs generally possess
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higher thermal and mechanical stability, and their viscosities are not significantly reduced
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under high temperature conditions, making them interesting materials for high temperature 4 ACS Paragon Plus Environment
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Analytical Chemistry
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applications. MILs have been more recently introduced and contain a paramagnetic
80
component in either the cation or the anion of the IL.6 Therefore, they can be manipulated
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using externally magnetic fields, making them particularly interesting in magnet-assisted
82
separation systems where the movement of flow or the MIL can be induced by the application
83
of static or dynamic magnetic field gradients.
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Studies involving ILs have impacted many areas of science, including material science,
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chemical engineering, environmental science, biochemistry, genetics, molecular biology, and
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chemistry. Thus, the number of scientific publications related to ILs have increased
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exponentially since 1992. Furthermore, in 2017 more than 6000 articles related to the topic
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of ILs have been published. In the field of analytical chemistry, the unique properties of ILs
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has led to their study in virtually every branch of the field, from sample preparation, mass
90
spectrometry and electrochemical sensing. The tuneability, versatility and selectivity of ILs
91
have been exploited in a wide variety of extraction and preconcentration methods7, including
92
both solid phase (micro)extraction8 and liquid phase (micro)extraction,9-11 to improve the
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resolution and efficiency of chromatographic12-14 and electrophoretic separations,15 as
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matrixes in mass spectrometry,16 and to provide high conductivity and wide electrochemical
95
windows in electrochemical sensing systems.17
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In 2014, we published a review included within the Fundamental and Applied Reviews in
97
Analytical Chemistry special issue of Analytical Chemistry in which the use of ILs in all of
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these areas was discussed.2 The current review provides an update to the fundamental study
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and applications of ILs in the field of analytical chemistry over the last several years. To
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address a rapidly growing area of study, we highlight new areas within bioanalysis where the
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unique features of ILs are being exploited.18 5 ACS Paragon Plus Environment
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Sample preparation
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Solid-phase (micro)extraction
105
Ionic liquids and polymeric ionic liquids in solid-phase extraction
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ILs and PILs are attractive materials for the development of solid-phase extraction (SPE)
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sorbents due to their easily tunable nature. In general, the majority of IL-based sorbent
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materials described in the literature are IL-modified silica sorbents, IL-modified polymers or
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IL-modified carbonaceous materials. This section summarizes the most recent applications
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regarding the use of IL-based sorbents for SPE and micro-SPE.
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Wang et al. functionalized polymethyl(methacrylate) with ILs for the post-combustion
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capture of carbon dioxide.19 The studied ILs were based on the 1-ethyl-3-methylimidazolium
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([C2MIM+]) cation paired with different amino acid-based anions (e.g., Lys, Gly, Ala, and
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Arg). The [C2MIM+][Lys-] IL was found to have the highest sorption capacity for CO2 (1.67
115
mmol·g-1 sorbent), which was explained by the multiple amine groups within the [Lys-] anion
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that can interact with CO2.
117
Metal determination is of particular significance as even trace amounts can have detrimental
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physiological effects in human health. Tokalıoğlu et al. developed a method for the
119
enrichment of Cu2+ and Pb2+ from water samples using IL-functionalized carbon nanospheres
120
(CNSs).20 An imidazolium-based IL containing the 1,8-napthalene monoimide functional
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group was used as a chelating agent towards metal ions within the CNSs. In this particular
122
study, the IL acted as a chelating agent of the metal ions. Limits of detection (LODs) of 0.30
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Analytical Chemistry
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and 1.76 µg L-1 were achieved for Cu2+ and Pb2, respectively. The method also proved to be
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resilient towards the addition of other monovalent and divalent metal ions.
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Wang et al. developed a low cost SPE sorbent by functionalizing luffa sponge fibers via
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physisorption of the 1-hexadecyl-3-methylimidazolium bromide ([C16MIM+][Br-]) IL.21 The
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sorbent was used in dispersive solid phase extraction (DSPE) for the determination of four
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common benzoyl urea pesticides from water and tea samples. By using only 70 mg of the
129
sorbent, LODs ranging from 0.14–0.21 µg·L-1 in water and from 0.19–0.23 µg·L-1 in tea were
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obtained. In another study, Zhang et al. developed IL-modified silica gel for the
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preconcentration of polyphenols from green tea leaves.22 The developed sorbent was able to
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extract and preconcentrate the target analytes with no significant decrease in antioxidant
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properties. The extraction mechanism was determined to be a combination of hydrogen
134
bonding, hydrophobic interactions, and π -π interactions.
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Zhang et al. developed a pipette-tip SPE method using an IL-functionalized graphene sorbent
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for the extraction of auxins from soybean sprouts.23 The sorbent was created by modifying
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the graphene surface with thiol groups via thiol-ene click chemistry. The modified graphene
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was subsequently reacted with the 1-allyl-3-pentafluorobenzylimidazolium bromide
139
([Al(BeF5)IM+][Br-]) IL and 2,2′-azobis(2-methylpropionitrile) (AIBN) to obtain the
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corresponding IL-functionalized thiol graphene. The IL prevented the aggregation of
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graphene while simultaneously affording the sorbent with π -π, ion exchange, and hydrogen
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bonding interaction capabilities. Good linearity was achieved using the optimized method,
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with LODs ranging from 2.6–4.0 ng g-1 for 1-naphthaleneacetic acid, 2,4-
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dichlorophenoxyacetic acid, and indole-3-acetic acid. Han et al. determined 6‑benzyladenine
145
and 4‑chlorophenoxyacetic acid in bean sprouts using an IL-hybrid molecular imprinted 7 ACS Paragon Plus Environment
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polymer (MIP).24 The prepared IL-hybrid MIP was capable of extracting 6‑benzyladenine
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through molecular recognition as the main mechanism while 4‑chlorophenoxyacetic acid was
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extracted via electrostatic and π -π interactions.
149
Ferreira et al. developed an fully automated online SPE method in combination with high-
150
performance liquid chromatography tandem mass spectrometry (HPLC-MS/MS) for the
151
determination
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butylsulfonateimidazolium ([VIMC4SO3-]) zwitterionic IL was synthesized and covalently
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confined to a silica substrate for the preparation of the packed SPE column. The developed
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material was employed in more than 100 sequential analyses without showing any loss of the
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extraction efficiency.
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Wang et al. recently developed crosslinked PIL microspheres based on the 1-vinyl-3-
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methylimidazolium hexafluorophosphate ([VMIM+][PF6-]) IL monomer for the rapid
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extraction of plasmid DNA from aqueous samples.26 Extraction/desorption of DNA was
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achieved by modulating the ionic strength of the solution. Low ionic strength conditions
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facilitated ion exchange between the anion of the PIL with the phosphate backbone of DNA.
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Conversely, high ionic strength (1 M NaCl) was used to strip DNA from the sorbent. The
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microspheres possessed high sorptive capacity (190.7 µg·mg-1) and excellent DNA
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recoveries (80.7%).
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For the extraction of proteins, Dang et al. synthesized a series of PIL sorbents containing 2-
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acrylamido-2-methylpropane sulfonate ([AMPS-])-based IL monomers with different cations
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(e.g. imidazolium, phenylimidazolium, and butylimidazolium).27 Sorption capacities for
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bovine hemoglobin as high as 983.4 mg·g-1 were achieved. Furthermore, the materials were
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capable of extracting hemoglobin directly from bovine blood followed by sodium dodecyl
of
the
antibiotic
ceftiofur
in
milk
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samples.25
The
1-vinyl-3-
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Analytical Chemistry
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sulfate–polyacrylamide gel electrophoresis (SDS-PAGE) and matrix-assisted laser
170
desorption/ionization- time of flight (MALDI-TOF) analysis, demonstrating the material’s
171
usefulness in complex matrixes.
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Dai et al. synthesized porous PILs by polymerizing the [VMIM+][Cl-] IL and ethylene glycol
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dimethacrylate within the framework of Mobil Composition of Matter No. 48 (MCM-48)
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spheres.28 This material was applied in on-line SPE of hydroxybenzoic acids from pollen
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extract. The extraction efficiency of the six studied analytes was not dependent on the pH of
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the extraction solution and an extraction time of 5 min was sufficient to reach equilibrium.
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Recoveries from pollen extract were acceptable for all analytes (82.7-102.4%) with LODs as
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low as 2 µg·L-1 for 4-hydroxybenzoic acid.
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On-line PIL-SPE has also been applied for the determination of antihypertensives in human
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plasma.29 A poly(IL-glycidylmethacrylate-co-ethyleneglycol dimethacrylate) monolithic
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SPE phase was prepared using the [VMIM+][Cl-] IL as a functional monomer. The optimized
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method extracted nifedipine, nitrendipine, and felodipine spiked in human plasma from
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patients that previously ingested nifedipine and nitrendipine tablets. In another application,
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Pang et al. used a similar PIL-monolithic column for the determination of steroid drugs in
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plasma.30 The monolith was based on the use of the 1-vinyl-3-hexylimidazolium bromide
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([VC6IM+][Br-])
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trimethylolpropane triacrylate as crosslinkers.
IL
as
functional
monomer
with
ethylenedimethylacrylate
188 189
Ionic liquids and polymeric ionic liquids in solid-phase microextraction
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Solid-phase microextraction (SPME) combines sample preparation and sampling resulting in
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reduced analysis times and increased sample throughput. The limited selection of
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commercially-available coatings necessitates the need for new sorbents with improved
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selectivity towards specific groups of analytes. ILs and PILs have been explored as sorbent
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coatings for SPME due to their tunable nature. This section provides an overview of IL- and
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PIL-based SPME sorbent coatings over recent years.
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Two recent studies have used ILs as SPME sorbents for the analysis of organophosphate
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esters in environmental water samples.31,32 Shi et al. used the 1-hexyl-3-methylimidazolium
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tris(pentafluoroethyl)trifluorophosphate ([C6MIM+][FAP-]) IL coated on a modified stainless
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steel wire.31 The extraction was performed in the direct immersion (DI)-SPME mode and
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subsequently coupled with gas chromatography (GC)-MS for the determination of
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organophosphate esters. The ultra-hydrophobicity and hydrolytic stability of the IL allowed
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for up to 65 consecutive extractions without a decrease in extraction efficiency. In another
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study, Pang et al. developed a hybrid SPME coating via sol-gel chemistry by combining a
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silica-based
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bis[(trifluoromethyl)sulfonyl]imide ([C16MIM+][NTf2-]) IL.32 For this application, HS-
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SPME was performed and LODs lower than 1 µg·L-1 for all of the studied analytes were
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obtained.
208
One significant area where PILs have been effectively utilized as sorbent coatings is in
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environmental analysis, where the robustness and unique selectivity afforded by PILs can
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facilitate the detection of many contaminants. Crosslinked PILs were effectively applied for
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the extraction of polar contaminants via DI-SPME in combination with HPLC- ultraviolet
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detection (UV).33 The crosslinked PILs were chemically attached to the surface of derivatized
material
with
the
1-hexadecyl-3-methylimidazolium
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Analytical Chemistry
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nitinol, which allowed the desorption of analytes from the fibers using organic solvents.
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Partition coefficients of the studied analytes showed that the developed PILs were especially
215
selective for the determination of polar compounds. An et al. recently developed PIL sorbent
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coatings that were remarkably stable under high ionic strength conditions (25% NaCl).34 The
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fibers were applied for the determination of UV filters from water samples using the DI-
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SPME mode in combination with HPLC-UV. By incorporating polymerizable styrene
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sulfonate anions into the PIL structure, the lifetime of the fibers increased drastically when
220
compared to analogous PIL fibers containing halide anions. Similarly, commercial fibers also
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exhibited significantly shorter lifetimes than the optimal PIL fiber. LODs as low as 0.2 µg
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L-1 were achieved using the newly developed PIL fibers. In another study, crosslinked PILs
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were successfully employed in headspace (HS)-SPME for the determination of UV filters in
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water samples with subsequent analysis by GC-MS.35 LODs in the range of 2.8–26 ng·L-1
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were achieved for the optimal PIL.
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Sun et al. developed graphene oxide (GO) reinforced PIL-SPME monoliths for the extraction
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of six phenolic compounds from environmental aqueous samples, followed by HPLC-UV.36
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To determine the effects of GO on the extraction of the target compounds, a comparison was
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made with neat PIL-SPME fibers and neat GO reinforced fibers. For the latter fibers, an order
230
of magnitude lower LOD was obtained. A multiple monolithic SPME phase based on the
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poly(1-allyl-3-methylimidazolium
232
dimethacrylate) polymer was used in DI-SPME in combination with HPLC-UV for the
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determination of steroid sex hormones.37 Similarly, other studies have focused on the
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extraction of endocrine disrupting chemicals (EDCs) with functionalized IL monoliths.38
bis[(trifluoromethyl)sulfonyl]imide-co-ethylene
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A new class of silver-based PIL sorbent coatings have been recently developed and applied
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in both HS- and DI-SPME.39 The sorbent coatings were based on IL monomers formed by
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cations containing the Ag+ ion coordinated with two 1-vinylimidazole ligands. The fibers
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were generated by polymerizing the silver-IL monomer in the presence of either [Ag+][NTf2-]
239
and/or a dicationic IL crosslinker. The fibers possessed adequate thermal stability (more than
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175 ºC) despite the presence of the Ag+ ions and were used for the determination of alkene
241
and alkyne mixtures with different degree of unsaturation via HS-SPME, and for the
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determination of oleic acid, linoleic acid and linolenic acid in wastewater via DI-SPME.
243
The identification and determination of contaminants in food is of importance for human
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health and safety. Recently, Cagliero et al. developed a PIL-SPME method for the
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determination of acrylamide in both brewed coffee and coffee powder.40 The PIL sorbent
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coatings used in this application were developed by a spin coating method, allowing for a
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larger film thickness. The developed DI-SPME-GC-MS method was able to detect
248
acrylamide with low limit of quantification (LOQ) (10 µg·L-1). This value was comparable
249
to the conventional ISO method for determining acrylamide while exhibiting a shorter
250
analysis time. In a subsequent study, nine PIL fibers were screened for the extraction of
251
acrylamide from coffee and compared to the best performing fiber from the initial study.41
252
Among all of the tested fibers, better extraction performance was achieved with the fiber
253
composed of 1,12-di(3-vinylbenzylimidazolium)dodecane [NTf2-] ([(VBeIM)2C122+]2[NTf2-
254
])
255
([V(C10OH)IM+][NTf2-]) IL monomer, with a LOQ as low as 0.5 µg L-1. Figure 2 shows GC-
256
MS chromatograms in the selected ion monitoring (SIM) mode obtained from the analysis of
257
blank and spiked brewed coffee samples using this PIL-sorbent coating.
as
the
IL
crosslinker
in
1-vinyl-3-(10-hydroxydecyl)imidazolium
12 ACS Paragon Plus Environment
[NTf2-]
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Hou et al. prepared hybrid SPME fibers based on GO-coated stainless steel wires modified
259
with either ILs or PILs for the determination of polycyclic aromatic hydrocarbons (PAHs)
260
and phthalate esters in food-wrap.42 Two different ILs, namely 1-aminoethyl-3-
261
methylimidazolium
262
methylimidazolium [NTf2-] ([(C2NH2)MIM+][NTf2-]), were directly attached to the GO
263
layer, while the two studied PILs, poly-1-vinyl-3-hexylimidazolium bromide (poly-
264
[VC6IM+][Br-]) and poly-1-vinyl-3-hexylimidazolium [NTf2-] (poly-[VC6IM+][NTf2-]), were
265
chemically attached by using the 3-mercaptopropyltriethoxysilane coupling agent. Recently,
266
Gionfriddo et al. exploited the tunability of PILs for both pesticide and metabolite analysis
267
from grape homogenate.43 The developed HS-SPME-GC-MS method required relatively
268
high temperatures (60 °C) due to the physicochemical properties of the analytes. The robust
269
nature of the PILs allowed for more than 20 extractions at this temperature without any loss
270
in the fiber performance. LOQs in the microgram per liter level were obtained for the studied
271
pesticides using the optimal PIL sorbent coating. In another study, PIL-SPME was performed
272
with comprehensive two-dimensional GC in combination with MS detection for the
273
characterization of the wine aroma profiles.44 This approach allowed for the identification of
274
>350 compounds from two different types of wine and facilitated their differentiation based
275
on their profiles.
276
ILs have also been explored as extraction phases for in-tube SPME. Sun et al. developed an
277
extraction phase by functionalizing copper wires with an imidazolium-based IL via thiol-ene
278
chemistry.45 The functionalized copper wires were subsequently placed in a copper tube to
279
create the in-tube sorbent. The developed in-tube SPME sorbent was applied for the
280
extraction of estrogens from water samples with acceptable recoveries (84–114%). In another
bromide
([(C2NH2)MIM+][Br-])
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and
1-aminoethyl-3-
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study, Feng et al. followed a similar strategy by functionalizing basalt fibers with
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imidazolium-based ILs.46 These sorbents were applied through in-line SPME-HPLC. The
283
extraction method was directly coupled to HPLC via a six-port valve, allowing for
284
automation. Other materials that have also been modified using ILs for SPME include carbon
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nanotubes (CNTs)47,48, polycarbazole49 and stainless steel tubes via physical adhesion.50
286
Souza et al. developed wall-coated open tubular capillary columns with PILs for the
287
determination of endocannabinoids in plasma samples.51 The inner wall of the capillary was
288
functionalized with vinyltrimethoxysilane (VTMS) and subsequently coated with a mixture
289
containing an IL monomer ([VC6IM+][Cl-] or [VC16IM+][Br-]), the 1,12-di(3-
290
vinylimidazolium)dodecane bromide [(VIM)2C102+]2[Br-] IL crosslinker, and AIBN as the
291
initiator. Following thermal polymerization, crosslinked PILs with a film thickness of 1.7 µm
292
were obtained. To achieve proper extraction of the selected group of analytes, pH 7 was
293
required. Extractions from plasma resulted in a wide linear range, from 0.05-100 ng mL-1.
294
A new class of electropolymerizable thiophene-functionalized PILs has recently been
295
developed and applied in HS-SPME.52 The thiophene ILs were prepared by reacting the
296
corresponding haloalkyloxythiophene with 1-methylimidazole, 1-vinylimidazole or 1-
297
benzylimidazole, followed by metathesis reaction with the [NTf2-] anion. Potential cycling
298
was subsequently applied on Pt wires covered in a solution of the IL to obtain the
299
corresponding PIL sorbent coatings. The resulting fibers possessed interesting
300
electrochemical properties and were also used for the determination of polar analytes. In
301
another study, Devasurendra et al. developed PILs based on the 3-(6-(1H-pyrrol-1-yl)hexyl)-
302
1-methyl-1H-imidazol-3-ium hexafluorophosphate ([pyrrole-C6MIM+][PF6-]) IL monomer
303
by its electro-polymerization on macro- and micro-electrode materials of Pt.53 The PILs were 14 ACS Paragon Plus Environment
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Analytical Chemistry
304
also doped with single walled carbon nanotubes (SWCNTs), where thicker PIL/SWCNT
305
films were obtained compared to polymerizing the neat IL (42 µm versus 17 µm). These
306
fibers possessed high selectivity and good fiber-to-fiber reproducibility for the extraction of
307
aromatic compounds.
308
PIL-based sorbent coatings have also been applied for the analysis of nucleic acids, yielding
309
a faster, more effective and reusable method in comparison to conventional liquid-liquid
310
extraction (LLE) and silica-based SPE approaches. The initial studies of Anderson and co-
311
workers were focused on the development and characterization of crosslinked PIL sorbent
312
coatings that possessed selectivity towards DNA and RNA.54,55 Real-time quantitative
313
polymerase chain reaction (qPCR) and reverse-transcription qPCR (RT-qPCR) were used to
314
evaluate the extraction performance of the fibers for DNA and RNA, respectively. Among
315
all of the tested crosslinked PILs, the highest extraction efficiency was achieved using the
316
fiber based on the 1-vinyl-3-decan-10-oic-imidazolium bromide ([V(C9COOH)IM+][Br-]) IL
317
monomer and the [(VIM)2C122+]2[Br-] IL crosslinker. The mechanism for nucleic acid
318
extraction was investigated by comparing the performance of the developed halide-based
319
PILs with analogous fibers containing the styrene sulfonate anion. The introduction of both
320
a polymerizable cation and anion in the structure of the PIL led to a drastic decrease in
321
extraction efficiency. This result indicated that the extraction mechanism of the fibers
322
towards nucleic acid could be a combination of both ion exchange and electrostatic
323
interactions. In a subsequent study, Varona et al. developed a PIL-SPME method for the
324
extraction of DNA from mycobacteria in artificial sputum at clinically relevant
325
concentrations (107 colony forming units mL-1).56 In this study, a vortex-assisted DI-SPME
326
method was employed for the extraction of DNA from lysed cells, resulting in faster
15 ACS Paragon Plus Environment
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327
enrichment of the nucleic acid, followed by isothermal multiple-self-matching-initiated
328
amplification (IMSA) using hydroxynaphthol blue (HNB) to afford the visual detection of
329
the amplified nucleic acid.
330 331
Liquid-phase (micro)extraction
332
Ionic liquids and magnetic ionic liquids in dispersive liquid-liquid microextraction
333
ILs have been extensively used in dispersive liquid-liquid microextraction (DLLME) for the
334
extraction and preconcentration of a wide variety of analytes. In the majority of the described
335
IL-DLLME applications, hydrophobic ILs are employed as extraction solvents. However,
336
hydrophilic ILs have also been exploited for in situ DLLME. In this DLLME mode, a
337
hydrophilic IL and metathesis reagent such as [Li+][NTf2-] is added to a sample solution,
338
allowing for the formation of microdroplets of hydrophobic IL containing the
339
preconcentrated analytes. In addition to the use of ILs and IL-based surfactants, an increasing
340
number of publications have described the use of MILs in DLLME. This section highlights
341
the use of ILs and MILs in DLLME in recent years, showing their applicability towards the
342
extraction of metal ions, organic pollutants, pharmaceuticals, and biomolecules.
343 344
Ionic liquid dispersive liquid-liquid microextraction
345
Cacho et al. developed an in situ DLLME method in combination with thermal desorption
346
gas chromatography-mass spectrometry (TD-GC-MS) for the determination of bisphenols.57
347
Different 1-alkyl-3-methylimidazolium chloride ([CnMIM+][Cl-], with n = 6, 8, 10 and 12)
348
ILs were used as extraction solvents. Derivatization of the analytes was performed prior to 16 ACS Paragon Plus Environment
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Analytical Chemistry
349
the DLLME step to increase the sensitivity of the method. LODs in the nanogram per liter
350
level were achieved from aqueous solutions. In addition, the method was effectively applied
351
for the analysis of plastic containers. Wang et al. developed a DLLME method for the
352
determination for bisphenols using the [C8MIM+][PF6-] IL.58 Analytes were extracted
353
through a combination of hydrophobic and hydrogen bonding interactions. The obtained
354
LODs ranged between 0.5 ng mL-1 for bisphenol A and 1.5 ng mL-1 for bisphenol AP.
355
ILs have also been employed as extraction solvents for in-syringe DLLME.59,60 For example,
356
Wang et al. developed an in-syringe in situ DLLME method for the extraction of benzoylurea
357
insecticides from honey samples.59 The procedure involved the metathesis reaction of the
358
tetrabutylammonium chloride ([N4,4,4,4+][Cl-]) IL with NaPF6 to generate the corresponding
359
water insoluble IL. The procedure utilized a medical syringe as the extraction vessel,
360
permitting the dispersion of the insecticide enriched-IL without the need of any dispersive
361
solvent or stirring, and its isolation without centrifugation. LODs ranging from 0.21–0.42 µg
362
L-1 were achieved with the method. In another application, Suárez et al. developed an on-line
363
in-syringe DLLME method for the extraction of UV filters.60 The [C6MIM+][PF6-] IL was
364
dispersed using a stir bar within a multi-syringe pump, followed by sequential dilution and
365
HPLC-UV analysis. Enrichment factors ranging from 11 to 23 were achieved for the six UV
366
filters. LODs in the microgram per liter level and adequate recoveries for the analysis in
367
seawater and swimming pool water were obtained.
368
The in situ DLLME mode was also applied towards the extraction of polychlorinated
369
biphenyls (PCBs) and acrylamide from coffee and milk samples.61 In this approach, the
370
analyte-enriched ILs were subjected to headspace sampling-GC-MS (HS-GC-MS),
371
facilitating desorption of the analytes from the IL to the headspace of the extraction vial while 17 ACS Paragon Plus Environment
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372
preventing the non-volatile ILs from entering the GC. LODs in the nanogram per liter and in
373
the microgram per liter level were achieved for PCBs and acrylamide, respectively. The
374
method was applied for the analysis of several food samples, including coffee and milk.
375
An effervescence-assisted IL-DLLME procedure was developed for the determination of
376
fungicides in environmental water samples.62 In this application, a magnetic effervescent
377
tablet composed of sodium carbonate and sodium dihydrogen phosphate as effervescent
378
precursors, the [C6MIM+][NTf2-] IL as extraction solvent, and Fe3O4 magnetic nanoparticles
379
were added to the aqueous solution containing the analytes. The reaction between the
380
effervescent precursors in water generated CO2 bubbles that assisted the homogeneous
381
dispersion of the IL in the sample. In addition, magnetic nanoparticles allowed the magnetic
382
separation of the analyte-enriched IL with the aid of a Nd-core magnet, thereby avoiding
383
centrifugation. LODs ranging between 0.02–0.10 g·L-1 and acceptable reproducibility and
384
recoveries were achieved.
385
Concerning the determination of metals, a gas assisted-DLLME method was developed for
386
the determination of Cu2+ from mineral water samples.63 Cu2+ was reduced to Cu+ using
387
hydroxylamine hydrochloride followed by its selective chelation using neocuproline and
388
extraction of the Cu+-complex using the [C6MIM+][PF6-] IL. Argon was used as a disperser
389
to eliminate the use of toxic organic solvents. The gas assisted-DLLME method was found
390
to achieve enrichment factors as high as 122 and no significant matrix effect was observed
391
in the analysis of mineral water.
392
Extraction from biological matrices can be difficult due to the high concentration of matrix
393
components such as albumin in plasma and serum samples or urea in urine. De Boeck et al.
394
used 1-alkyl-3-methylimidazolium [PF6-] ([CnMIM+][PF6-], with n = 4, 6, 8) ILs, together 18 ACS Paragon Plus Environment
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Analytical Chemistry
the
1-butyl-1-methylpyrrolidinium
[NTf2-]
([C4MPy+][NTf2-])
and
the
395
with
396
butyltrimethylammonium [NTf2-] ([N1,1,1,4+][NTf2-]) ILs for the determination of
397
antidepressants in whole blood.64 After 5 min of mixing, the IL was diluted in methanol and
398
subjected to liquid chromatographic analysis (LC-MS/MS). Among the studied ILs, the
399
[C4MIM+][PF6-] IL provided the smallest chromatographic background with seventeen of the
400
eighteen tested antidepressants being properly analyzed in tablets.
401
Wang et al. developed an ultrasound-assisted IL-DLLME method for the determination of
402
triclosan and methyltriclosan using a system composed of the [C8MIM+][PF6-] IL as
403
extraction solvent and a mixture of the [C4MIM+][BF4-] and 1-butyl-3-methylimidazolium 1-
404
naphthoic acid salt ([C4MIM+][NPA-]) ILs as disperser solvents.65 Ammonium
405
hexafluorophosphate was also added during the extraction as an ion pair reagent. Adequate
406
recoveries and LODs between 0.12–0.15 µg L-1 in plasma and urine samples were achieved.
407
In another application, the low cytotoxic decylguanidinium chloride ([C10Gu+][Cl-]) IL was
408
used as extraction solvent in salt-induced DLLME for the determination of a group of
409
hydroxylated PAHs in urine samples.66 The preconcentration method is similar to the in situ
410
DLLME mode; however, NaClO4 was used to promote the insolubility of the IL, avoiding
411
the use of toxic fluorine-based salts that are often employed in other in situ DLLME methods.
412
LODs ranging from 0.5 to 1 ng·L-1 and adequate precision was achieved.
413
The methyltrioctylammonium thiosalicylate ([N1,8,8,8+][TSC-]) TSIL was applied in a
414
DLLME method in combination with electrothermal atomic absorption spectroscopy
415
(EAAS) for the extraction of Cd2+ from human blood, serum, and urine samples.67 This TSIL
416
permitted Cd2+ to be extracted without a chelating agent. At the same time, the ammonium-
417
based IL provided higher extraction efficiency than analogous imidazolium-based ILs. 19 ACS Paragon Plus Environment
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418
Fernández et al. employed the [C6MIM+][NTf2-] IL to extract Hg2+ from urine samples using
419
vortex-assisted DLLME.68 Ammonium pyrrolidinedithiocarbamate was used as a chelating
420
agent to aid the partitioning of Hg2+ to the hydrophobic IL phase. The Hg2+-complex was
421
then re-extracted from the IL-rich phase using HCl and detected using a gold nanoparticle
422
modified screen printed electrode. The obtained LODs in urine ranged from 0.5–1.5 µg L-1.
423
Arain et al. extracted Cu2+ from drinking water and serum samples of hepatitis C patients
424
using a microemulsion-DLLME method.69 The [C4MIM+][PF6-] IL was used as extraction
425
solvent while Triton X-100 was used to stabilize the generated microemulsion by reducing
426
the interfacial tension of the IL. Cu2+ was extracted to the IL phase using 8-hydroxyquinoline
427
as a chelating agent. The Cu2+-complex rich-IL was isolated using micellar cloud point
428
extraction (MCPE), followed by flame atomic absorption spectroscopy (FAAS). Enrichment
429
factors as high as 7 and a LOD of 0.132 µg L-1 were obtained.
430 431
Magnetic ionic liquid dispersive liquid-liquid microextraction
432
The inherit magnetism of MILs makes them attractive extraction solvents in DLLME. For
433
that reason, an increasing number of publications within the past several years have reported
434
MIL-DLLME methodologies. In these applications, magnetic separation is carried out to
435
recover the MIL solvent after extraction, eliminating the need of centrifugation and filtration
436
steps that are often necessitated with DLLME procedures.6,18,70,71 Table 1 includes several
437
applications that use MILs in DLLME and other liquid-phase microextraction (LPME)
438
techniques.72-84
439
MIL-DLLME has been applied for the determination of PAHs in environmental water and
440
tea.72 Three different iron-based MILs were studied as possible extraction solvents, including 20 ACS Paragon Plus Environment
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Analytical Chemistry
441
two
monocationic
442
([N8,8,8,B+][FeCl3Br-])
443
([N8,8,8,MOB+][FeCl3Br-]), and a dicationic MIL, 1,12-di(3-benzylbenzimidazolium)dodecane
444
[NTf2-] [FeCl3Br-] ([(BBnIM)2C12+][NTf2-][FeCl3Br-]). It is interesting to mention that the
445
mixed anions of the [(BBnIM)2C12+][NTf2-][FeCl3Br-] MIL aided in controlling the
446
hydrophobicity of the solvent. The highest extraction performance was achieved using the
447
[N8,8,8,B+][FeBrCl3-]
448
tetrachloromanganate(II) ([MnCl42-])-based MILs as extraction solvents in DLLME for the
449
determination of pharmaceutical drugs, phenolics, insecticides, and PAHs.73 The [MnCl42-]-
450
based MILs exhibited less UV absorption and limited hydrolysis in water, which are
451
advantages over MILs based on tetrachloroferrate (III) ([FeCl4-]) and [FeCl3Br-]. Adequate
452
analytical performance was observed using the [MnCl42-]-based MILs with LODs ranging
453
from 0.25 to 1.00 µg L-1.
454
Chisvert et al. developed an extraction method termed stir bar dispersive liquid extraction
455
(SBDLME) for the determination of PAHs.74 In this approach, the MIL solvent was dispersed
456
using a Nd-core magnetic stir bar at high stirring rates. Under these stirring rates, the MIL
457
was dispersed in the sample solution as fine microdroplets. When the stirring was stopped,
458
the analyte-enriched MIL was collected by the stir bar due to its magnetic attraction. The stir
459
bar was subsequently subjected to TD-GC-MS analysis. For this application, the studied
460
MILs
461
([P6,6,6,14+][Ni(hfacac)3-]),
462
([P6,6,6,14+][Co(hfacac)3-]),
463
([P6,6,6,14+][Dy(hfacac)4-]). These MILs exhibited lower viscosity in comparison to the
were
MILs,
benzyltrioctylammonium
and
MIL
bromotrichloroferrate
[FeCl3Br-]
methoxybenzyltrioctylammonium
for
all
of
the
trihexyl(tetradecyl)phosphonium [P6,6,6,14+] and
PAHs
tested.
Yu
(III)
et
al.
studied
tris(hexafluoroacetylaceto)nickelate(II) tris(hexafluoroacetylaceto)cobaltate(II)
[P6,6,6,14+]
tris(hexafluoroacetylaceto)dysprosate(III)
21 ACS Paragon Plus Environment
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Page 22 of 99
464
previous generations of MILs, which facilitated the dispersion of the MIL during the
465
extraction and, as a consequence, improved the extraction performance of the method.
466
Several MIL-DLLME methods have also been developed for the determination of
467
biomolecules. Clark et al. utilized thiol-ene click chemistry to synthesize ion-tagged
468
oligonucleotides (ITO) capable of selectively annealing to complementary DNA sequences.75
469
Once
470
tris(hexafluoroacetylaceto)manganate(II) ([P6,6,6,14+][Mn(hfacac)3-]) MIL, which exhibited
471
low DNA extraction efficiency without the ITO. Hydrophobic interactions between the ITO
472
and MIL were largely responsible for the capture of ITO by the MIL. The MIL-ITO
473
procedure was found to outperform commercial magnetic beads when extracting target DNA
474
in the presence of background DNA and in complex matrices. In a similar approach, Peng et
475
al. found that the [P6,6,6,14+][Co(hfacac)3-] MIL exhibited high extraction efficiencies for poly-
476
cytosine (poly-C) tagged DNA oligonucleotides.76 DNA oligonucleotides were designed
477
containing a complementary sequence to the target DNA and a poly-C tail. The poly-C tagged
478
duplex was found to selectively extract approximately 300-fold more DNA compared to a
479
direct extraction method without the poly-C probe. Higher extraction efficiencies were also
480
achieved when extractions were performed with the poly-C tagged oligos in the presence of
481
background DNA.
482
Different MILs were also studied as solvents in DLLME for the extraction of viable E. coli
483
cells.77 The [P6,6,6,14+][Ni(hfacac)3-], [P6,6,6,14+][Co(hfacac)3-], [P6,6,6,14+][Dy(hfacac)4-], and
484
[P6,6,6,14+] tetrakis(hexafluoroacetylaceto)dysprosate(III) ([P6,6,6,14+][Nd(hfacac)4-]) MILs
485
were capable of extracting viable cells from aqueous solutions for detection using either
486
culture or qPCR-based detection methods. Enrichment factors as high as 44.6 were achieved
hybridized,
the
duplex
was
capable
of
partitioning
22 ACS Paragon Plus Environment
to
the
[P6,6,6,14+]
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Analytical Chemistry
487
using the [P6,6,6,14+][Ni(hfacac)3-] MIL in less than 10 min. Preconcentration of the E. coli
488
cells using the MIL-DLLME method allowed for lower LOD using qPCR compared to direct
489
sampling of the aqueous cell suspensions, suggesting that this method has potential for
490
detecting food-borne pathogens.
491
MIL-DLLME was designed for the extraction of the hormones estriol and extrone in urine
492
samples
493
tetrachloromanganate(II) [Aliquat+]2[MnCl42-] MILs.78 Estriol was detected in an unspiked
494
urine sample from a pregnant volunteer, indicating that the MIL-DLLME method is a viable
495
approach towards extracting hormones from complex biological samples.
using
the
[P6,6,6,14+]2[MnCl42-]
and
trioctylmethylammonium
496 497
Ionic liquids and magnetic ionic liquids in single-drop microextraction
498
Although both hydrophobic and hydrophilic ILs have been used in single-drop
499
microextraction (SDME),9 the majority of reported applications in recent years using SDME
500
with IL-based materials have utilized MILs as extraction solvents (Table 1). In MIL-SDME
501
applications, a rod Nd-core magnet aids in suspending the MIL directly in the aqueous
502
solution or in the headspace of the extraction vial, depending on the SDME mode. With this
503
configuration, a higher microdroplet volume can be suspended from the rod magnet for
504
prolonged sampling time, even under strong stirring.
505
An et al. compared the extraction performance of MIL-HS-SDME and MIL-DLLME for the
506
determination of 12 aromatic compounds.79 Two different MILs, namely [P6,6,6,14+]2[MnCl42-]
507
and [Aliquat+]2[MnCl42-], were studied. The results indicated that the optimized HS-SDME
508
procedure provided higher enrichment factors for volatile aromatic compounds, whereas the
23 ACS Paragon Plus Environment
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Page 24 of 99
509
MIL-DLLME procedure was effective for the extraction of analytes possessing low vapor
510
pressures.
511
In another application, the [P6,6,6,14+][Mn(hfacac)3-] MIL was used in HS-SDME under low
512
pressure conditions (vacuum HS-SDME).82 The procedure was compared with the
513
conventional HS-SDME method under atmospheric conditions for the determination of short
514
chain free fatty acids. It was concluded that the vacuum HS-SDME method reached
515
equilibrium faster while providing low LODs, in the range of 14.5 to 216 g·L-1.
516
In
517
tetraisothiocyanatocobaltate(II) ([C2MIM+]2[Co(NCS)42-]) MIL was applied in HS-SDME
518
for the extraction of nine chlorobenzenes from tap, pond, and wastewater.83 The extraction
519
was accomplished in only 10 min, with LODs ranging from 4-8 ng L-1.
520
Several MIL-SDME methods have been developed for the analysis of biomolecules. Emaus
521
et al. developed a DI-SDME method to extract short cell-free DNA fragments.80 The DNA-
522
enriched MIL was incorporated into a specially designed qPCR buffer to remove the need
523
for an added DNA desorption/recovery step. The results indicated that the addition of the
524
MIL did not affect the amplification efficiency during qPCR. The MIL method was compared
525
to commercial magnetic beads used for DNA extraction and similar extraction efficiencies
526
for double stranded DNA were observed. However, the magnetic beads significantly
527
decreased the amplification efficiency of qPCR when they were directly added to the qPCR
528
reaction.
529
MIL-SDME was also applied towards the extraction of DNA from a cell lysate, followed by
530
thermal desorption of DNA during loop-mediated isothermal amplification (LAMP) and
531
isothermal multiple-self-matching-initiated amplification (IMSA).81 The addition of MILs to
another
study,
the
hydrophilic
24 ACS Paragon Plus Environment
1-ethyl-3-methylimidazolium
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Analytical Chemistry
532
the amplification buffer resulted in reduced background fluorescence associated with primer-
533
dimer based nonspecific amplification and allowed for the visual detection of PCR products.
534 535
Ionic liquids in hollow fiber liquid-phase microextraction
536
ILs have been used as extraction solvents in both two-phase and three-phase hollow fiber
537
liquid-phase microextraction (HF-LPME).9 Among the common advantages of ILs as
538
extraction solvents, the elevated viscosity of ILs prevents their loss during the extraction,
539
allowing for higher extraction efficiencies and better reproducibility. This section
540
summarizes recent applications involving the use of ILs in HF-LPME in both modes.
541 542
Two phase ionic liquid-hollow fiber liquid-phase microextraction
543
The two phase HF-LPME system is comprised of an acceptor phase located within the lumen
544
of a porous fiber and the donor phase (i.e., the sample). This microextraction mode has been
545
applied towards the extraction of Co2+ and Ni2+ from human urine samples.85 The chelating
546
agent 1-(2-pyridylazo-2-naphthol (PAN) was added to the sample solution to aid in the
547
partitioning of Co2+ and Ni2+ to the hydrophobic [C6MIM+][PF6-] IL phase. NaPF6 was also
548
added to the sample to assist in ion-pairing with the Co2+ and Ni2+ anions. LODs as low as
549
0.09 and 0.03 ng mL-1 for Co2+ and Ni2+, respectively, were obtained using FAAS with
550
enrichment factors ranging from 66-82 in human urine.
551
One limitation of HF-LPME is the potential loss of the extraction phase during the extraction.
552
To combat this, López-López et al. sealed both ends of the HF containing the IL extraction
25 ACS Paragon Plus Environment
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553
solvent to prevent the IL from leaching into the sample solution during the extraction.86 In
554
this application, the trioctylmethylammonium thiosalicylate ([Aliquat+][TS-]) and
555
trioctylmethylammonium 2-(methylthio)benzoate ([Aliquat+][MTBA-]) ILs were capable of
556
extracting Cd2+, Cr4+, Cu2+, Ni2+, and Pb2+ with the HF-LPME method while [P6,6,6,14+]-based
557
ILs were able to quantitatively extract Ag+ after a 24 h extraction.
558 559
Three phase ionic liquid-hollow fiber liquid-phase microextraction
560
In three phase HF-LPME, also called liquid-liquid-liquid microextraction (LLLME), the
561
extraction phase is not in direct contact with the donor phase and acts as a supported liquid
562
membrane (SLM) on the HF. An extra component, the acceptor phase, is used during the
563
extraction. Analytes undergo partitioning from the donor phase to the extraction phase and
564
finally to the acceptor phase. Wang et al. developed a three-phase HF-LPME approach for
565
the determination of phthalate esters from tea using the [C4MIM+][PF6-] IL as acceptor
566
phase.87 The high viscosity of the IL prevented the loss of the acceptor phase into the aqueous
567
solution during the extraction but also prevented the IL from fully impregnating the
568
membrane pores. In this application, 1-nonanol was used as the SLM phase to ensure higher
569
recoveries. Enrichment factors as high as 200 were achieved. In another study, the
570
trioctylmethylammonium chloride ([N1,8,8,8+][Cl-]) IL was employed in HF-LPME for the
571
extraction of tetracyclines from diluted milk samples.88 The donor solution was pumped
572
though the fiber and subsequently eluted with the aid of a peristaltic pump. The results
573
indicated the tetracyclines formed an ion pair complex with the [N1,8,8,8+] cation during the
26 ACS Paragon Plus Environment
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Analytical Chemistry
574
extraction process. Relative recoveries in diluted milk ranged between 92–108% with the
575
proposed method.
576
Pimparu et al. developed an on-line HF-LPME method for the extraction of Cr6+ from
577
environmental water samples using the commercial Aliquat 336 IL as a SLM.89 In the
578
reported method, the HF was attached to a six-port injection valve and multi-position
579
selection valve, and the donor solution flowed outside of the HF while the acceptor phase
580
flowed within the membrane’s lumen. A 1,5-diphenylcarbazide solution was injected onto
581
the membrane to chelate the metal, and the Cr6+-complex was subsequently detected using
582
UV-vis spectroscopy. The HF-IL-LPME method allowed for a 41-fold enrichment with
583
LOQs below the maximum allowable concentration of Cr6+ set by the California
584
Environmental Protection Agency (EPA). Alahmad et al. developed an IL-HF-LPME
585
method using the Aliquat® 336 IL as extraction phase and NaCl as acceptor solution for the
586
extraction of Cr6+.90 The extraction was facilitated using an ion exchange transport process
587
through the IL support, and spectroscopic detection was performed using 1,5-
588
diphenylcarbazide as chelating agent. Enrichment factors as high as 60 were achieved,
589
allowing for faster visual detection of the Cr6+-complex.
590 591
Ionic liquids and magnetic ionic liquids in aqueous biphasic systems
592
ILs have been used as phase-forming components in aqueous biphasic systems (ABS) to
593
introduce polarity differences in the two phases that constitute the ABS, in general salt-salt,
594
salt-polymer, or polymer-polymer.91-93 In addition, the structural tailoring ability of ILs make
595
them ideal for ABS to impart selectivity towards specific analytes. For these reasons, IL-
27 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
596
ABS have been developed and applied for the extraction, preconcentration and/or
597
purification of metal ions, organic compounds and biomolecules.
598
The majority of applications describing the extraction and separation of metal ions have
599
utilized acidic water/IL or salt/water/IL systems for developing the ABS.93,94 In these studies,
600
the addition of the acid (or the salt) prevented hydrolysis and precipitation of the target metal
601
ions while promoting the formation of metal complexes able to be extracted into the IL-rich
602
phase. For example, Gras et al. developed an ABS based on HCl and the
603
tributyltetradexylphosphonium chloride ([P4,4,4,14+][Cl-]) IL for the extraction of Ni2+, Co2+,
604
Pt4+ and Fe3+.94 It was found that under elevated temperatures Ni2+ could be separated into
605
the HCl-rich phase while Co2+, Pt4+, and Fe3+ were extracted into the [P4,4,4,14+][Cl-]-rich
606
phase, as demonstrated in Figure 3. Separation was facilitated by the formation of metal
607
chloride complexes able to undergo ion exchange with the [P4,4,4,14+][Cl-] IL. Chen et al.
608
separated Nd3+ from Co2+ and Ni2+ using an ABS based on the tetrabutylphosphonium nitrate
609
([P4,4,4,4+][NO3-]) IL and NaNO3.95 The extraction of metal ions to the IL-rich phase was
610
achieved through an anion exchange mechanism, resulting in a 96% extraction efficiency of
611
Nd3+ compared to only 7.8% and 5.9% for Co2+ and Ni2+, respectively. Nd3+ was selectively
612
extracted because Co2+ and Ni2+ ions were unable to form anionic metal complexes capable
613
of undergoing ion exchange with [P4,4,4,4+][NO3-]. In addition, the possibility of recovering
614
and reusing the IL in successive extractions was possible by using oxalic acid to precipitate
615
the extracted Nd3+.
616
Speciation of metal ions is of importance as detection methods such as EAAS and inductively
617
coupled plasma-mass spectrometry (ICP-MS) cannot differentiate between oxidation states.
618
Therefore, Sadeghi et al. designed an IL-ABS using the [C8MIM+][salicylate-] TSIL, sodium 28 ACS Paragon Plus Environment
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Analytical Chemistry
619
acetate and Triton X-114 to selectively extract Cr3+ while leaving the mutagenic Cr4+ in the
620
aqueous layer.96 The IL-ABS approach was able to extract 11.1% of Cr4+ and 92.5% of Cr3+
621
from aqueous solution.
622
Dimitrijević et al. used an IL-ABS containing the 1-butyl-3-ethylimidazolium dicyanamide
623
([C4C2IM+][DCA-]) IL and K2CO3 for the extraction of pesticides of varying polarity.97
624
Quantitative extraction was achieved using the [C4C2IM+][DCA-]-ABS, likely because the
625
IL exhibited higher binding energies towards acetamiprid and imidacloprid. In another study,
626
aluminum-based salts used as coagulants/flocculants in wastewater treatment were employed
627
in an IL-ABS approach to extract fluoroquinolones.98 Different imidazolium- and
628
phosphonium-based ILs were examined in this application, and extraction efficiencies
629
ranging from 27.6 to 97.8%, depending on the IL, were achieved. The extraction efficiency
630
decreased with increasing chain length of the imidazolium cation and increased when the
631
anion contained an aromatic functional group. Fluoroquinolones were subsequently
632
recovered by its precipitation using K3PO4 and the IL could be reused without losses in its
633
extraction performance.
634
A pH-driven ABS using imidazolium-, piperidinium-, pyrrolidinium- or phosphonium-based
635
ILs along with citrate/citric acid were applied for the separation of dehydrate fructose and 5-
636
hydroxy-methylfurfural.99 In this study, 5-hydroxy-methylfurfural was extracted into the IL-
637
rich phase with extraction efficiencies of 92–96 % while fructose preferred the salt-rich phase
638
(45–59% extraction efficiency) due to differences in polarity.
639
Quental et al. developed an ABS extraction method using tetraalkylphosphonium or
640
tetraalkylammonium-based ILs and carbohydrates.100 Carbohydrates acted as salting-out
641
agents due to the number and positioning of alcohol groups. The developed IL-ABS method 29 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
642
extracted 65–99% of the antioxidants gallic acid, syringic acid, and vanillic acid through
643
hydrogen bonding, hydrophobic interactions, and dispersion forces. Antioxidants were
644
subsequently recovered from the IL-rich phase using SPE.
645
The 1,1,3,3-tetramethylguanidinium 2,2,6,6-tetramethylpiperidine ([TMG+][TEMPO-SO3-])
646
MIL was used as an ABS component for the extraction of chloramphenicol from
647
environmental water samples.84 This MIL was designed without any paramagnetic metal in
648
the cationic/anionic moieties. The developed biphasic system was formed by the addition of
649
K3PO4 in the aqueous solution of the MIL. ABS extraction was accomplished in only 1 min,
650
and the MIL-phase was then isolated with the aid of an external magnet. A LOD of 0.14 ng
651
mL-1 and relative recoveries in river and lake water ranging from 94.6–99.7% were achieved.
652
Since ABS are mainly composed of water, they can be considered biocompatible systems for
653
biomolecules such as proteins, enzymes, antibodies, and nucleic acids.91 Bogdanov et al.
654
investigated the use of an IL-ABS containing the choline saccharinate ([Ch+][Sac-]) IL and
655
Na2CO3 for the extraction of the acetylcholinesterase inhibitors galantamine N-desmethyl
656
galantamine and ungiminorine.101 Enrichment factors as high as 153 were achieved, and no
657
matrix effect was observed when the method was applied for the analysis of Nivalin pills.
658
Acceptable recoveries were also noted when applying the IL-ABS extraction method towards
659
human urine. Zawadzki et al. developed an IL-ABS method for the extraction of amitriptyline
660
hydrochloride, an antidepressant drug, using a biphasic system composed by either
661
[N4,4,4,4+][Cl-] or [N4,4,4,4+][Br-] with K2HPO4/KH2PO4.102 The phosphate salts promoted
662
salting out of the desired analytes to the IL-rich phase. The analytes were then re-extracted
663
from the IL-rich phase by adjusting the pH. The optimized extraction procedure was capable
664
of quantitatively extracting the antidepressant drugs from ADT 25 mg pills. 30 ACS Paragon Plus Environment
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Analytical Chemistry
665
Yang et al. extracted L-phenylalanine as a model amino acid in an IL/polymer/inorganic salt
666
ABS.103 Different imidazolium-based ILs were introduced to the polymer-rich phase to better
667
tune the physicochemical properties of the PEG600-rich phase. Generally, imidazolium
668
cations with longer alkyl chain length substituents resulted in an increased partition
669
coefficient of L-phenylalanine to the IL/polymer phase, with the exception of the 1-decyl-3-
670
methylimidazolium chloride ([C10MIM+][Cl-]) IL. Introducing the more hydrophobic acetate
671
anion into the IL structure also effected the partition coefficient to the IL/polymer-rich phase.
672
ILs have also been used as adjuvants in a polyethylene glycol (PEG) 3350/(NH4)2SO4 ABS
673
for the extraction of myoglobin.104 In this study, it was concluded that the addition of shorter
674
alkyl chains within imidazolium ILs enhanced the two-phase separation. Therefore, the
675
addition of 5 wt% of the IL adjuvant increased the extraction efficiency from 9.96% to
676
62.7%, whereas the addition of 7.5 wt% of the 1-butyl-3-methylimidazolium acetate
677
([C4MIM+][CH3CO2-]) IL resulted in the quantitative extraction of myoglobin.
678
A series of Good’s buffers ILs (GBILs) were designed by Gupta et al. to act as buffers during
679
the ABS extraction of α-chymotrypsin.105 The GBILs maintained a constant pH in the ABS,
680
preventing conformation changes of the enzyme and the loss of its activity while also
681
providing quantitative extraction of α-chymotrypsin.
682
IL-ABS have also been applied towards the purification of IgG antibodies.106 ABS composed
683
of polypropylene glycol and different choline-based ILs were able to quantitatively extract
684
IgG from both aqueous solutions and rabbit serum samples. In addition, the ABS did not
685
affect the stability of the IgG antibody when the choline glycolate ([Ch+][Gly-]) and choline
686
L-ascorbate ([Ch+][Asc-]) ILs were used as extraction solvents.
687
Chromatographic and electrophoretic separations 31 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
688
Gas chromatography
689
ILs have been studied as stationary phases in GC and multidimensional GC (MDGC) due to
690
their high thermal stability, high polarity, and tunable selectivity.14,107-109 An important
691
number of publications have examined the polarity of the developed IL-based stationary
692
phases and have compared then to conventional stationary phases. The commercially-
693
available IL-based columns from Millipore Sigma (e.g., SLB-IL59, SLB-IL100, and SLB-
694
IL111) utilize the polarity number (PN) reported by Mondello and co-workers.110 In addition
695
to the PN, the Abraham solvation parameter model provides unique insights into the solvation
696
capabilities of the IL-based GC columns. The Abraham model characterizes the solvation
697
properties of the IL-based stationary phases towards analytes by measuring five different
698
types of interactions, namely, π-π or n-π interaction, polarizability/dipolarity, hydrogen
699
bonding basicity and acidity of the stationary phase, and dispersive-type interactions. Lenca
700
and Poole have thoroughly investigated different commercial IL-based columns, including
701
SLB-IL60, SLB-IL61, and SLB-IL76 using the solvation parameter model.111-113 Other
702
important parameters of IL-based stationary phases are the operating temperature range,
703
column efficiency, peak symmetry, and inertness. Among these, the thermal stability is of
704
specific importance for high temperature applications.114,115 This section describes recent
705
publications that examine IL-based stationary phases for both GC and MDGC.
706 707
Monocationic ionic liquid-based stationary phases
708
GC applications examining monocationic IL stationary phases have utilized different
709
combinations of cations (e.g., phosphonium, ammonium, sulfonium, imidazolium, and
710
pyridinium) and anions (e.g., halide, triflate – [TfO-], tetrafluoroborate – [BF4-], 32 ACS Paragon Plus Environment
Page 32 of 99
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Analytical Chemistry
711
hexafluorophosphate – [PF6-], and [NTf2-]). Recently, a number of studies using
712
phosphonium-based ILs have appeared as these ILs typically exhibit higher thermal stability
713
than ammonium or imidazolium-based ILs.116 Hantao et al. employed different IL-based GC
714
stationary phases for the separation of aliphatic hydrocarbons by comprehensive two-
715
dimensional gas chromatography (GC × GC).117 The GC stationary phases based on
716
trihexyl(tetradecyl)phosphonium
717
[P6,6,6,14+][FAP-] ILs provided the better separation of aliphatic hydrocarbons compared to
718
commercial columns (e.g., OV-1701, SUPELCOWAX10, SLB-IL60, SLB-IL100, and SLB-
719
IL111). High thermal stability was also achieved with these stationary phases (with
720
maximum allowable operating temperatures, MAOT, of 320 ºC). Despite the fact that most
721
IL-based stationary phases are used as wall coated open tubular (WCOT) columns, Regmi et
722
al. described the coating of two different ILs, namely [P6,6,6,14+][NTf2-] and 1-butylpyridinum
723
[NTf2-] ([C4Py+][NTf2-]), into the channels of micro-fabricated semi-packed columns (SPCs)
724
for GC.118 The developed IL-coated SPCs produced sharp and symmetrical peaks, offered
725
high separation efficiency, and increased the separation speed.
726
ILs containing imidazolium cations are generally the most widely examined IL-stationary
727
phases;
728
decomposition/volatilization at elevated temperature. To further improve their thermal
729
stability as well as the separation performance, Pello-Palma et al. reported a covalently
730
bonded IL-based GC stationary phase for the determination of volatile compounds in cider
731
apple juices.119 The stationary phase was prepared by covalently reacting the imidazolium
732
monolith to the free silanol groups within the inner capillary surface. The developed IL
733
stationary phase exhibited a thermal stability up to 290 ºC and column efficiency of 2000
however,
they
are
tetrachloroferrate(III)
also
among
the
most
33 ACS Paragon Plus Environment
([P6,6,6,14+][FeCl4-])
susceptible
at
and
the
undergoing
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
734
plates·meter-1. In a similar application, Dai et al. immobilized the 1-butyl-3-[(3-trimethoxy-
735
silyl)propyl]imidazolium chloride ([C4((MOSi)3C4)IM+][Cl-]) IL onto the inner wall of a
736
fused-silica capillary to improve thermal stability.120 However, peak tailing of common
737
analytes such as octane and butanol was observed to be a major challenge for further
738
application. Nan et al. reported lipidic imidazolium IL-based stationary phases for the
739
determination of aliphatic hydrocarbons by GC × GC.121 These ILs possessed long alkyl side
740
chains (from C16 to C18) as well as low melting points, which provided enhanced dispersive-
741
type interactions suitable for the separation of aliphatic hydrocarbons in the second
742
dimension.
743 744
Di- and polycationic ionic liquid-based stationary phases
745
Dicationic ILs have been known to exhibit significantly higher thermal stability compared to
746
traditional monocationic ILs.115,116 The thermal decomposition pathways of various
747
dicationic ILs were thoroughly investigated by Patil et al.114 In this study, the selectivity of
748
nine different dicationic imidazolium and pyrrolidinium IL-based stationary phases was
749
examined. In a subsequent study using the same stationary phases performed by the same
750
authors, it was concluded that the polarity of the stationary phase was affected by the choice
751
of cations and anions as well as the length of the alkyl linker chain.122 Talebi et al. reported
752
twelve dicationic IL-based stationary phases for the separation of fatty acid methyl esters
753
(FAMEs).123 Structural differences of the alkyl linker chain were found to strongly influence
754
both the polarity and selectivity of the stationary phase in the separation of FAMEs. Several
755
physicochemical properties including viscosity, density, and thermal stability of branched-
756
chain ILs were also reported.124 Jiang et al. investigated the separation performance and 34 ACS Paragon Plus Environment
Page 34 of 99
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Analytical Chemistry
757
solvation properties of four different geminal ILs with p-xylene as linker chain.125 These ILs
758
exhibited excellent separation performance for aromatic positional isomers. In addition, the
759
ILs containing [NTf2-] anions possessed better selectivity for alcohols and aromatic positional
760
isomers compared to ILs comprised of [BF4-] and [PF6-] anions. Heydar et al. reported a new
761
dicationic IL with naphthalenyl moieties.126 McReynolds constants and the Abraham
762
solvation parameter model were used to characterize the polarity of the IL-based stationary
763
phase. The developed stationary phases possessed an average polarity of 667 (PN = 75), and
764
presented strong intermolecular interactions (dipole-dipole, H-bonding basicity and
765
dispersive-type interactions) with analytes. The study also suggested that the IL-based
766
stationary phase is especially suitable for the separation of polyaromatic compounds. Talebi
767
et al. investigated the effect of anionic moieties on the thermal stability and selectivity of
768
dicationic IL-based stationary phases.127 Unique selectivities toward unsaturated FAMEs and
769
PAHs were observed when employing these ILs with different anion moieties. Among the
770
developed
771
fluorosulfonylalkylated anion exhibited the highest thermal stability (above 300 ºC).
772
Mono- and dicationic pyridinium IL-based GC columns were employed as the first
773
dimension column for the separation of phenol-containing pyrolysis products using GC × GC
774
with the pyridinium IL × HP-5 column set.128 Compared to the ZB-Wax × HP-5 column set,
775
the dicationic pyridinium IL × HP-5 column set provided better performance in the separation
776
of diaromatics and phenols, especially for the 2,4-dimethylphenol/ 4-methylphenol pair. The
777
separation was achieved due to the high polarity of the IL and the low contribution of
778
dispersive-type interactions compared to the ZB-WAX column.
GC
stationary
phases,
dicationic
ILs
779
35 ACS Paragon Plus Environment
containing
the
symmetrical
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
780
Polymeric ionic liquid-based stationary phases
781
The polymerization of IL cations/anions to produce PILs is a strategy to increase the thermal
782
stability of IL-based stationary phases and to reduce their tendency of pooling or forming
783
droplets at high temperatures. Roeleveld et al. developed two PIL-based stationary phases
784
via both the chain-growth and step-growth methods.129 The results indicated that PILs
785
generated by the step-growth method produced higher thermal stability (up to 325 ºC)
786
compared to the chain-growth PIL (decomposition temperature of 250 ºC).
787
Zhang et al. examined a crosslinked PIL-based stationary phase for the GC × GC separation
788
of kerosene and diesel.130 The crosslinked PIL-based stationary phase possessed a MAOT of
789
325 ºC and provided better selectivity in the separation of aliphatic hydrocarbons when it
790
was used as the second-dimension column compared to the commercial carbowax and DB-
791
17 columns.
792 793
Metal-containing ionic liquid-based stationary phases
794
Metal salt additives have been reported to exhibit a significant effect on the selectivity of GC
795
stationary phases and have historically been widely used in packed GC columns.131,132
796
However, few studies have reported the use of metal salt additives in WCOT columns due to
797
their limited solubility and poor mixing in traditional stationary phases.133,134 Metal-
798
containing ILs are a subclass of ILs containing a metal center in either the cation or the anion.
799
These ILs are liquids at room temperature despite incorporating a metal center, making them
800
of interest in GC applications. Anderson and co-workers have studied silver-based ILs with
801
various chelating ligands to separate paraffin and olefins.135 These stationary phases were
36 ACS Paragon Plus Environment
Page 36 of 99
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Analytical Chemistry
802
found to be highly selective in the separation of volatile hydrocarbons of various size and
803
containing double and triple bonds of varied geometry. In another study, different metal-
804
containing IL stationary phases with transition and rare earth metals (e.g., Ni2+, Mn2+, and
805
Dy3+) coordinated with different chelating ligands were investigated.136 The stationary phases
806
were characterized by the Abraham solvation parameter model. The results showed
807
significant differences in the solvation properties depending on both the metal center and the
808
ligand employed to generate the metal-containing IL. The Mn2+-based IL stationary phase
809
possessed the highest hydrogen bonding basicity, where the Dy3+-based column provided
810
higher dipolarity/polarizability. Higher hydrogen bonding acidity was also observed when
811
the hexafluoroacetylacetonate ligand was coordinated with the metal, in comparison to a
812
similar IL with no ligands.
813 814
Commercial ionic liquid-based stationary phases
815
In the last several years, new IL-based columns have been introduced to the market. The
816
Watercol series of columns were developed and introduced specifically for the analysis of
817
water. In addition, IL-stationary phases within the i-series (e.g., SLB-IL76i and SLB-IL11i)
818
have been developed to provide enhanced inertness to previous versions of structurally
819
similar stationary phases. Finally, a new IL-based stationary phase intended for separating
820
mixtures of PAHs, namely SLB-ILPAH, has become commercially- available. Recent
821
applications of these stationary phases, along with new applications of IL-based commercial
822
columns, are summarized in this section.
823
Armstrong and co-workers developed water-compatible IL-based stationary phases
824
(commercially available as Watercol 1460, Watercol 1900, and Watercol 1910) for the 37 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 38 of 99
825
separation and detection of trace water, with a working range between 12–3258 mg·kg-1 (see
826
Figure 4).137-139 The precision of the method was verified by using NIST and American
827
Society for Testing and Materials (ASTM) methods. The analysis of samples containing
828
water presents another major challenge. When conventional stationary phases are employed,
829
direct injection of aqueous samples is normally avoided since water induces peak asymmetry,
830
poor sensitivity and efficiency, strong adsorption, as well as stationary phase degradation.
831
Cagliero et al. demonstrated that water compatible IL-based columns can be routinely used
832
for the direct analysis of samples with water as the main solvent, making them very promising
833
for the analysis of fragrances and essential oils.140
834
The inertness of IL-based columns is a major concern for end-users. Studies have shown that
835
IL-based stationary phases provide excellent resolution and efficiency, but their lack of
836
inertness can make them less attractive.141 To overcome this limitation, different inert IL-
837
based
838
MilliporeSigma in 2016. Retention times and elution orders of analytes separated on these
839
new inert columns were highly comparable with the previous generation of stationary phases.
840
However, significantly reduced peak widths, peak tailing, and lower column bleed was
841
observed, making them very attractive to complex sample analysis. These columns were
842
further examined for the analysis of fragrance and essential oils.142 It was found that the inert
843
stationary phases are highly competitive with most of the common PDMS or PEG-based
844
columns. Pojjanapornpun et al. evaluated the separation performance of the SLB-IL111i
845
stationary phase for the separation of FAMEs using GC × GC.143 Compared with the previous
846
generation SLB-IL111 column, the SLB-IL111i stationary phase exhibited reduced column
847
bleed, higher profiling speed, and better repeatability. Figure 5 shows representative contour
columns
(SLB-IL60i,
SLBIL76i,
and SLB-IL111i)
38 ACS Paragon Plus Environment
were introduced by
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Analytical Chemistry
848
plots of a 37 FAME mix obtained with the SLB-IL111i stationary phase in the first dimension
849
combined with different IL-based stationary phases in the second dimension. Less bleeding
850
can also be observed with the inert SLB-IL111i stationary phase (see Figure 5c versus Figure
851
5d).
852
IL-based GC columns are commonly used as alternatives to PEG-based stationary phases in
853
applications where both high polarity and high thermal stability are needed. IL-based GC
854
columns have been widely applied for the analysis of FAMEs using one dimensional GC as
855
well as MDGC.13,144-146 In one dimensional GC applications, Gómez-Cortés et al. employed
856
the SLB-IL111 stationary phase to discriminate odd and branched-chain fatty acids from
857
other milk fatty acids eluting within the same chromatographic regions.144 IL-based
858
stationary phases have also been applied for the analysis FAMEs in GC × GC.145-147 Marriot
859
and co-workers developed a heart-cutting MDGC-MS method with a unique column set (100
860
m HP-1 PONA × 30 m SLB-IL60) to analyze trace-level contamination of FAMEs in diesel
861
fuel.147 In this application, the SLB-IL60 stationary phase provided unique selectivity, high
862
polarity, and high thermal stability (with MAOT of 300 °C). The obtained LODs of
863
individual FAMEs ranged from 0.5 to 5.0 mg·L-1, which was two orders of magnitude lower
864
than previously reported methods.
865
Sciarrone et al. reported a MDGC method using a combustion-isotope ratio MS/ quadrupole
866
MS (C-IRMS) detector and a low-bleed SLB-IL59 second dimension column for the analysis
867
of food products containing truffles.148 In comparison to a PEG column, the IL-based
868
stationary phase provided lower noise at the elution temperature of vanillin (about 210 °C).
869
This high efficiency MDGC-C-IRMS system was applied for monitoring of bis(methylthio)-
39 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
870
methane, which is responsible for the white truffle aroma. The analyte was successfully
871
resolved from other components in different commercial products investigated in the study.
872
Ramos and co-workers examined six IL-based stationary phases for the separation and
873
detection of a mixture of 69 environmentally-related polychlorinated biphenyls (PCBs).149
874
Different selectivity was achieved depending on the employed GC stationary phase. In
875
addition, it was found that the SLB-IL59 stationary phase was able to resolve the most toxic
876
non-ortho congeners (77, 126, and 169) from other PCBs in the test mixture.
877
Wilson et al. investigated the retention behavior of polycyclic aromatic sulfur heterocycles
878
(PASHs) on IL-based GC columns.150-151 The retention index of 10 sets of alkyl-substituted
879
PASH isomers (total of 80 PASHs) and 48 polycyclic aromatic PASHs were determined
880
using the commercial SLB-ILPAH stationary phase.
881 882
High Performance Liquid Chromatography
883
High performance liquid chromatography (HPLC) is a major analytical technique used for
884
the separation of complex mixtures of analytes. In HPLC, ILs have been used as mobile phase
885
modifiers, substituting for conventional organic modifiers such as acetonitrile, methanol or
886
tetrahydrofuran. They have also been employed in low concentrations as mobile phase
887
additives, pseudo-stationary phases in micellar liquid chromatography (MLC), and as
888
components of the stationary phase. Table 2 shows representative applications in which ILs
889
have been studied with these purposes in HPLC within the period between 2016-2018. Most
890
of the literature within this time period deals with the use of ILs as mobile phase additives or
891
as components in stationary phases.152-161
40 ACS Paragon Plus Environment
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Analytical Chemistry
892 893
Ionic liquids as mobile phase additives
894
ILs have been added at low concentrations to the mobile phase in HPLC separations to
895
suppress the effect of free silanol groups in common silica-based stationary phases. In these
896
cases, the IL cation can strongly interact with the stationary phase by an ion exchange
897
process, thereby masking or blocking the residual free silanol groups of the phase. As a result,
898
the chromatographic behavior is often improved with regard to the peak shape, resolution,
899
band broadening, and analysis time.
900
Caban and Stepnowski have studied the effect of both the cation and anion of the IL in the
901
mobile phase for the separation of tri-cyclic basic antidepressants by reversed phase (RP)-
902
HPLC.162 The authors hypothesized that typical anions of ILs (e.g. [PF6-] > perchlorate,
903
[ClO4-] > trifluoroacetate, [CF3COO-], chloride, [Cl-] > acetate, [HCOO-] >
904
dihydrogenphosphate, [H2PO4-], in agreement with the Hofmeister series) can influence the
905
retention of the analytes. In these cases, the anions break the solvation shells around the
906
analytes, making them more hydrophobic resulting in improved retention in RP-HPLC.
907
Binary mobile phases of acetonitrile and different aqueous phases containing the
908
[C4MIM+][Cl-] or the [C4MIM+][PF6-] ILs were evaluated in the study. Overloading studies
909
of clomipramine revealed that the IL-based mobile phases possessed a higher sample loading
910
capacity than conventional mobile phases containing ammonium acetate and triethylamine-
911
based compounds.
912
The majority of the reported studies regarding this field have utilized imidazolium- or
913
ammonium-based ILs.162 However, a new class of TSILs as terpene derivatives (1-
914
[(1R,2S,5R)-(−)-menthoxymethyl]-3-methylimidazolium chloride, [(CH2O-Men)MIM+][Cl41 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
and
Page 42 of 99
915
],
1-[(1R,2S,5R)-(−)-menthoxymethyl]-3-pentylimidazolium
916
Men)C5IM+][Cl-]) were used as mobile phase additives to enhance the separation of acidic
917
enantiomers on a glycopeptide stationary phase.152 It was proved that the addition of the
918
chiral [CH2O-MenC5IM+][Cl-] IL to the mobile phase was responsible for the best
919
improvement in the enantioresolution of the analytes. Docking simulations of the system
920
were in agreement with the obtained chromatographic results. In another study, geminal
921
dicationic ILs based on imidazolium, piperidinium, morpholinium, pyrrolidinium,
922
piperazinium, and ammonium cations were used as mobile phase additives in RP-HPLC for
923
the separation of auxinic herbicides, a group of polar compounds with high acidic character
924
that are extremely difficult to separate using traditional C18 silica stationary phases.153
925
Analyte retention in these separations was modulated by repulsive forces between the IL
926
cation / anion and analytes present in their neutral form, hydrophobic interactions between
927
the carbon chains of the IL and the neutral analytes, and ionic interactions with ionized
928
analytes.
929
Deep eutectic solvents (DES) based on ILs have also been added as additives to the mobile
930
phase for the separation of bioactive quaternary alkaloids by RP-HPLC.154 The studied DES
931
were
932
tetraalkylammonium chloride ([Nn,n,n,n+][Cl-], with n = 1, 2 or 3) ILs at different ratios. The
933
ILs acted as hydrogen bond acceptors in the DES while ethylene glycol, urea, citric acid or
934
glycerol were used as hydrogen bond donors. The results demonstrated that the addition of
935
DESs to the mobile phase at the appropriate pH improved the separation of these basic
936
compounds. LODs between 0.006 and 0.020 µg·mL-1 were achieved, and both herbal oral
937
solutions and tablets were successfully analyzed with the method.
prepared
by
mixing
either
choline
chloride
42 ACS Paragon Plus Environment
chloride,
([Ch+][Cl-])
or
[(CH2O-
different
Page 43 of 99 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
938
ILs have also been employed to improve the separation of metal ions.155,163 Mercury and its
939
different chemical species Hg2+, methylmercury (CH3Hg+) and ethylmercury (C2H5Hg+),
940
were determined by RP-HPLC with UV and cold vapor generation atomic fluorescence
941
spectrometry (CV-AFS). In this study, the separation was achieved using mobile phases
942
composed of methanol and citric acid/citrate buffer in an aqueous solution of NaCl in which
943
different ILs were used as additives.155 The studied ILs included on [CnMIM+][Cl-] (with n
944
=4, 6, 8, and 12) and tributylmethylphosphonium methylsulfate ([P4,4,4,1+][CH3SO4-]). With
945
regards to the imidazolium-based ILs, the proposed mechanism for the successful separation
946
of ions began with the formation of negatively charged chlorocomplexes with the mercury
947
ions, followed by ion-pairing with the IL cations and their retention on the C18 stationary
948
phase. In another application, mobile phases composed of several 1-alkyl-3-
949
methylimidazolium tetrafluoroborate ([CnMIM+][BF4-], with n = 2,3,4 or 6) ILs and oxalic
950
acid were used in ion chromatography for the determination of alkaline earth metal ions,
951
including Mn2+, Ca2+, and Sr2+.163 Indirect UV detection of the ions was possible because the
952
ILs within the mobile phase served as background UV absorption reagents. Separation of the
953
ions using a carboxylic acid cation exchange column was achieved due to the presence of
954
oxalic acid. The length of the alkyl substituent of the imidazolium cation also influenced the
955
retention behavior of the metal ions. Therefore, a decrease in the retention times of the ions
956
was observed with increased length. The authors noted that stronger bonding of ILs to the
957
ion exchange sites of the stationary phase resulted when larger ILs were added as additives
958
to the mobile phase, causing a decrease in the retention of the ions of interest.
959
In addition to HPLC, ILs have been applied as mobile phase additives in high-performance
960
thin-layer chromatography (HPTLC) for the determination of haloperidol and its two
43 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
961
metabolites in human plasma.156 In particular, the studied analytes were separated on glass
962
plates percolated with silica gel in a glass chamber using a mobile phase consisting of
963
acetonitrile: water: 1-ethyl-3-methylimidazolium tetrafluoroborate ([C2MIM+][BF4-])
964
(50:50:1.5, v/v). The separation was achieved in only 25 min, and the HPTLC was coupled
965
with MS to increase the sensitivity of the method. In another study, mobile phases containing
966
ILs were used in two-dimensional TLC (2D-TLC) for the separation of alkaloids and its
967
identification in plant extracts.164 The separations were performed on glass cyanopropyl
968
plates using a mixture of methanol, diisopropyl ether, ammonia and acetic acid in the first
969
dimension, and acetonitrile, water, formic acid, and 1-butyl-3-methylimidazolium
970
tetrafluoroborate ([C4MIM+][BF4-]) in the second dimension.
971 972
Ionic liquids as components of the stationary phase
973
ILs have been used as structural components in HPLC stationary phases. A wide number of
974
applications have developed surface-confined ionic liquid (SCIL) stationary phases by
975
attaching the IL to a silica substrate using a coupling agent, in general, a type of
976
organoalkoxysilane. For the synthesis of the corresponding SCIL, both monomeric or
977
polymeric processes have been employed. Qiao et al. reported SCIL stationary phases using
978
an amide-functionalized imidazolium IL.157 A monomeric heterogeneous process was used
979
for the preparation of the stationary phase, with (3-mercaptopropyl)trimethoxysilane being
980
employed as a coupling agent followed by thiol-ene click chemistry for grafting the IL onto
981
the surface of the modified silica. The developed stationary phases were successfully applied
982
in hydrophilic interaction liquid chromatography (HILIC) for the separation of flavonoids in
983
soybean and urine samples. 44 ACS Paragon Plus Environment
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Analytical Chemistry
984
Chiral SCIL stationary phases based on IL chiral selectors were prepared and applied for the
985
enantioseparation of chiral acids.165 The IL chiral selectors were prepared by the ring opening
986
of cyclohexene oxide with imidazole or 5,6-dimethylbenzimidazole, and then chemically
987
modified with different substituent groups. The main driving force of the separations using
988
these chiral stationary phases was ion exchange, and retention in the chiral acids was
989
influenced by the type of substituent and the counterion of the chiral SCIL. In another study,
990
a chiral SCIL stationary phase was prepared by the modification of oxazolinyl-substituted -
991
cyclodextrin with a pyridinium IL followed by its covalent bonding to silica.158 Excellent
992
enantioseparations were achieved using this chiral stationary phase. The IL introduced a
993
stronger electrostatic effect onto the stationary phase, making it suitable for the separation of
994
polar compounds.
995
Wang, Xu and Xue developed a zwitterionic SCIL stationary phase based on quaternary
996
ammonium, a tertiary amine, and sulfonate groups.159 The stationary phase acted as a RPLC/
997
HILIC mixed-mode stationary phase and was especially selective for the separation of polar
998
and ionizable analytes. In addition, the stationary phase separated six non-steroidal anti-
999
inflammatory drugs (NSAIDs) from plant extracts. The separation was achieved in less than
1000
20 min using a gradient linear elution of a binary mobile phase composed of an aqueous
1001
solution of ammonium formate and acetonitrile.
1002
Wu et al. prepared stationary phases based on IL/graphene quantum dots/silica
1003
composites.160 The stationary phases were evaluated in different separation modes, including
1004
normal phase (NP)-LC, RP-LC, ion exchange chromatography (IEC), and HILIC. The
1005
stationary phase was also compared with analogous graphene quantum dots/ silica or IL/
45 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1006
silica phases. The results indicated that the combination of both materials had a synergistic
1007
and complementary effect in the separation of the studied analytes.
1008
The aforementioned applications utilized packed SCIL stationary phases based on ILs. As an
1009
alternative, other applications have reported the development and use of monolithic
1010
stationary phases based on ILs.161,162 Han et al. developed a polyhedral oligomeric
1011
silsesquioxane-based hybrid monolithic column that contained the L-cysteine hydrochloride
1012
amino acid and the [VC4IM+][Br-] IL as functionalized monomers.161 The monoliths were
1013
prepared in an one step process via free radical co-polymerization using the thiol-ene click
1014
reaction. The stationary phases were used for different applications in capillary
1015
chromatography, including the separation of alkylbenzenes and hydrophilic amides with
1016
mobile phases composed of acetonitrile and water, the purification of the TARG1 protein, an
1017
adenosine diphosphate ribose protein glycohydrolase, as well as the separation of a group of
1018
glycoproteins (ovalbumin, horseradish peroxidase and -transferring) and non-glycopotreins
1019
(ribonuclease A, bovine serum albumin, BSA, and myoglobin). The selectivity of the
1020
developed stationary phase was directly related to the presence of the amino acid, while
1021
stronger retention of proteins was linked to the nature of the IL. In another study, a polymer
1022
monolith was prepared using the 1-allyl-3-methylimidazolium chloride ([AMIM+][Cl-]) IL
1023
and triallyl isocyanurate as monomers, ethylene dimethacrylate as crosslinker, and different
1024
porogen components.166 The stationary phases presented uniform macroporous structures,
1025
which resulted in better chromatographic efficiency than traditional polymer monoliths
1026
prepared via similar polymerization procedures.
1027 1028
Counter-current chromatography 46 ACS Paragon Plus Environment
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Analytical Chemistry
1029
ILs have been added as modifiers in biphasic liquid systems used in counter-current
1030
chromatography (CCC). For example, a Cu2+ complexed amino acid IL, namely Cu(II)-[1-
1031
butyl-3-methylimidazolium][L-proline] (Cu(II)-[C4MIM+][L-Pro-]), was added as a
1032
modifying additive in high speed CCC to improve the enantioseparation of naringenin, a
1033
flavanone found in citrus fruits.167 The biphasic system used in this application was
1034
composed of a n-heptane- ethyl acetate- acetonitrile - 0.2 mol·L-1 sodium acetate aqueous
1035
solution (7:3:3:7, v/v/v/v) at pH 5.5. The system contained the chiral IL selector together
1036
with hydroxypropyl--cyclodextrin. UV-vis absorption and NMR studies demonstrated that
1037
the chiral recognition mechanism resulted from the formation of a quaternary complex
1038
composed of Cu2+, the chiral IL, hydroxypropyl--cyclodextrin, and naringenin.
1039
In another study, a method was developed using CCC as a sample pretreatment step followed
1040
by HPLC for the enrichment of mycotoxins in wine and juice.168 The biphasic system was
1041
composed of ethyl acetate- water (1:1, v/v), which contained the IL. Among the different
1042
imidazolium-based ILs tested as modifiers, the 1-carboxymethyl-3-methylimidazolium
1043
chloride ([(HOOCM)MIM+][Cl-]) IL provided the highest enrichment of the mycotoxins,
1044
with partition coefficients to the ethyl acetate layer ranging from 297 to 3478 and LODs of
1045
the entire CCC-HPLC methodology ranging from 0.03 to 0.14 g·L-1. The results also
1046
indicated that both the nature of the cation and anion of the IL significantly impacted the
1047
extraction efficiency of the mycotoxins.
1048
Müller et al. reported IL-based biphasic systems for CCC that were applied for the
1049
purification of extremely non-polar lipid compounds, followed by GC-MS.169 Miscibility
1050
studies were conducted to select the most suitable biphasic system for the separation of the
1051
analytes. The obtained results showed that the system comprised of n-heptane- chloroform47 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1052
1-decyl-3-methylimidazolium trifluoromethanesulfonate ([C10MIM+][TfO-]) (3:3:1, v/v/v)
1053
provided a partial separation of tripalmitin and cholesteryl stearate, highlighting that ILs are
1054
suitable for use in non-polar CCC.
1055 1056
Capillary electrophoresis
1057
ILs with high conductivity and tunable miscibility can serve as excellent additives in capillary
1058
electrophoresis (CE). In particular, an important number of studies have used ILs as
1059
background electrolytes. In these applications, the IL cations can interact with deprotonated
1060
silanol groups on the capillary surface in order to modify the electroosmotic flow. In addition,
1061
various chiral cations and anions have been investigated in chiral CE separations. The
1062
applications of ILs in CE have been summarized by Holzgrabe et al. in 2016.170 This section
1063
describes the most recent developments of IL-assisted CE analysis.
1064
Imidazolium-based ILs are generally the most commonly used in CE. Kolobova et al. used
1065
different imidazolium-based ILs as dynamic and covalent modifiers within the background
1066
electrolyte for the separation of catecholamines.171 IL coatings prevented sorption of
1067
catecholamines on the inner capillary wall resulting in improved separation efficiency and
1068
peak symmetry. Memon et al. used the [C4MIM+][PF6-] IL as an additive in CE for the
1069
separation of flavonoids.172 The results indicated that the IL improved separation and reduced
1070
analysis time. The separation was achieved due to the formation of an electrically neutral
1071
single layer of the imidazolium cations on the inner capillary, resulting in faster migration of
1072
the negatively charged flavonoids.
48 ACS Paragon Plus Environment
Page 48 of 99
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Analytical Chemistry
1073
Chiral IL additives have attracted significant attention in CE enantioseparations.15,173 The
1074
majority of studies combined the use of cyclodextrins (CDs) with ILs as chiral selectors in
1075
the CE buffer. Greño et al. have compared the enantioseparation of homocysteine using either
1076
neutral CDs or chiral ILs as CE chiral selectors.174 The best enantioseparation was achieved
1077
using a combination of the (R)-N,N,N-trimethyl-2-aminobutanol [NTf2-] IL and β-CD as
1078
chiral selectors in a phosphate run buffer (pH 7.0). Interestingly, the migration order of the
1079
D- and L-homocysteine enantiomers was reversed when both selectors were added in
1080
comparison to the order obtained when a chiral selector was employed. Wahl et al. studied
1081
ILs with [N4,4,4,4+] cations and chiral amino acid-based anions as background electrolyte
1082
additives for the electrophoretic enantioseparation of ephedrine, pseudoephedrine, and
1083
methylephedrine isomers.175 The best separation was obtained using a combination of the
1084
[N4,4,4,4+] L-argininate ([N4,4,4,4+][L-Arg-]) IL and β-CD in phosphate buffer (pH 1.5). Wang
1085
et al. employed hydroxypropyl-β-CD (HP-β-CD) and the [N4,4,4,4+] L-glutaminic acid
1086
([N4,4,4,4+][L-Glu-]) IL as additives in the separation of corynoxine and corynoxine B using
1087
field-amplified sample stacking (FASS)-CE.176 The combination of FASS as a
1088
preconcentration technique and CE provided a 700–900 fold increase in the sensitivity
1089
(stacking efficiency). Yang et al. designed two hydroxy acid-based chiral ILs, namely,
1090
tetramethylammonium D-pantothenate ([N1,1,1,1+][D-PAN-] and [N1,1,1,1+] D-quinate
1091
([N1,1,1,1+][D-QUI-]), as chiral additives together with maltodextrin as co-selectors in CE.177
1092
The addition of the IL to the maltodextrin chiral CE system significantly improved the
1093
separation of four racemic drugs (nefopan, ketoconazole, econazole, and voriconazole). Li et
1094
al. used a newly synthesized amino triazolium functionalized β-CD derivative (mono-6-
1095
deoxy-6-(4-amino-1,2,4-triazolium)-β-cyclodextrin chloride) for the enantioseparation of
49 ACS Paragon Plus Environment
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1096
dansyl amino acids and naproxen by CE.178 This IL functionalized chiral selector exhibited
1097
enhanced enantioselectivity and improved solubility in water.
1098 1099
Mass spectrometry
1100
Mass spectrometry (MS) is among the most powerful analytical techniques employed for the
1101
characterization of a wide range of compounds, ranging from small organic molecules to
1102
large biomolecules such as proteins and nucleic acids. ILs have been applied in MS as ionic
1103
matrixes for matrix-assisted laser desorption ionization mass spectrometry (MALDI-MS)
1104
and as additives in electrospray ionization mass spectrometry (ESI-MS). This section
1105
summarizes developments in the last several years regarding these two areas.
1106
Ionic liquids as matrixes in matrix-assisted laser desorption ionization
1107
MALDI-MS is often used for imaging applications and for the analysis of large molecular
1108
weight compounds. MALDI utilizes a pulsed laser along with a matrix (often organic) to aid
1109
in the desorption and ionization of the analyte(s) of interest. Some disadvantages of
1110
commonly used organic matrixes include lack of matrix spot-homogeneity and low
1111
ionization efficiency of some analytes. IL matrixes have continued to be successfully applied
1112
for both large biomolecule characterization as well as for the analysis of organic molecules
1113
and polymers.
1114
Ling et al. employed an IL matrix based on the 1,1,3,3-tetramethylguanidinium salt of 2,4,6-
1115
trihydroxyacetophenone for the MALDI-MS detection of phosphopeptides in the negative
1116
ion mode.179 Adding phosphoric acid resulted in a significant enhancement to the signal-to-
1117
noise (S/N) ratio when compared to S/N ratios resulting from the neat IL. Another study used
50 ACS Paragon Plus Environment
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Analytical Chemistry
1118
ILs as a derivatizing agent prior to analysis by MALDI-MS.180 The method used ILs with
1119
allyl functional groups to break apart Cys-Cys disulfide bridges through thiol-ene click
1120
chemistry. The resulting proteins undergo in-source decay and allow for easy identification
1121
of mutation sites due to higher fragmentation.
1122
Carbohydrate analysis with MALDI-MS is a challenge due to low ionization efficiency when
1123
conventional matrixes are employed. Zhao et al. demonstrated that IL matrixes can be used
1124
to improve carbohydrate analysis with MALDI-MS.181 A set of 12 ILs possessing 2,5-
1125
dihydroxybenzoate ([DHB-]) anions and different cations were synthesized. When
1126
maltohexaose was analyzed, the IL matrixes [DHB-]/N-methylaniline (N-MA) and [DHB-]/
1127
N-ethylaniline (N-EA) provided LODs of 10 fmol, which was two orders of magnitude lower
1128
than the standard [DHB-] matrix. The stark difference in ionization efficiency can be
1129
observed in Figure 6, where analysis of neutral polysaccharides (D2000 and D4000) was
1130
enhanced using IL matrixes ([DHB-]/N-MA and [DHB-]/N-EA) compared to [DHB-]. One
1131
possible explanation for this enhancement is that the developed [DHB-]/N-MA and [DHB-
1132
]/N-EA matrixes possess higher absorbances, 0.555 and 0.538, respectively, than DHB
1133
(0.404) at a laser wavelength of 355 nm.
1134
Leipert et al. developed a method using an IL matrix for the detection of Pseudomonas
1135
aeruginosa virulence factors and bacterial communication molecules.182 The method
1136
consisted of a rapid DLLME procedure to isolate the compounds of interest followed by
1137
MALDI-MS analysis. A α-cyano-4-hydroxycinnamic acid/3-aminopentane matrix was
1138
synthesized and found to be the most efficient IL matrix for the analytes of interest. Once
1139
optimized, the method was used to detect three target molecules (2-heptyl-4(1H)-quinolone
1140
and 2-heptyl-3-hydroxy-4(1H)-quinolone) in clinical sputum samples from cystic fibrosis 51 ACS Paragon Plus Environment
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1141
patients. Furthermore, quantification of the virulence factor pyocyanin formed by the Gram-
1142
negative bacterium Pseudomonas aeruginosa was achieved by using internal standards. In
1143
another study, an IL matrix was used to generate a high throughput matrix-enhanced
1144
secondary ion mass spectrometry (ME-SIMS) method for single cell profiling of neuronal
1145
cells.183 Abdelhamid et al. developed a series of IL matrixes by ultrasonication and applied
1146
them for the analysis of bacterial toxins without requiring any sample pretreatment.184 The
1147
use of these matrixes allowed for the efficient ionization of the toxins even in the presence
1148
of macromolecules.
1149
Shrivas et al. developed a DLLME method using an IL-matrix for the extraction and
1150
subsequent detection of phospholipids in soybean by MALDI-MS.185 A two-fold benefit was
1151
observed in using the IL as both matrix and extraction solvent, as the analytes were first
1152
preconcentrated and then efficiently ionized with the matrix. Kosyakov most recently
1153
employed IL matrixes for the analysis of lignin.186
1154
MALDI-MS is commonly used for the analysis and characterization of polymers. However,
1155
the analysis is often hindered by the lack of spot homogeneity which leads to irreproducible
1156
results. Gabriel et al. studied several IL matrixes for the analysis of polymers that possessed
1157
higher homogeneity than traditional matrixes.187 Furthermore, low laser power could be used
1158
while maintaining a high response, decreasing polymer fragmentation. In another study, the
1159
quantitative analysis of polyhexamethylene guanidine oligomers via MALDI-TOF was
1160
possible by using a 1‐methylimidazolium α‐cyano‐4‐hydroxycinnamate IL matrix.188 In this
1161
application, higher reproducibility was obtained when compared to an analogous
1162
α‐cyano‐4‐hydroxycinnamate matrix, likely due to improved spot homogeneity.
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Analytical Chemistry
1163
The analysis of small molecules using MALDI-MS poses a challenge due to high background
1164
interference in the lower m/z region of the mass spectrum. Highly stable matrixes with low
1165
background are therefore highly desired for small molecule analysis. Liu et al. recently
1166
developed a hybrid material by immobilizing α‐cyano‐4‐hydroxycinnamate and (3-
1167
aminopropyl)triethoxysilane on a TiO2 surface.189 This matrix possessed a lower background
1168
than traditional α‐cyano‐4‐hydroxycinnamate matrixes while enhancing the signal for the
1169
studied analytes.
1170 1171
Ionic liquids as additives in electrospray ionization mass spectrometry
1172
Electrospray ionization (ESI) is a commonly used soft-ionization technique for the analysis
1173
of large biomolecules. A solution is flowed through a thin capillary in which a voltage is
1174
applied. This potential difference generates charged droplets to the entrance of the mass
1175
spectrometer that undergo evaporation to produce gas phase ions. The identification of
1176
compounds at the level of tissues and single-cells normally provide insufficient signal
1177
intensity in MS or high matrix interference, particularly when the low-intensity target signals
1178
overlap with high-intensity signals of other substances present in the cells. To overcome this
1179
limitation and improve the LODs in ESI-MS, drugs in the IL-form have been designed.
1180
Kucherov et al. synthesized a mitoxantrone-IL tagged conjugate and studied its cytotoxic
1181
behavior and detection using ESI-MS.190 By using the 1-decanoic-3-methylimidazolium
1182
[BF4-] ([(C9COOH)MIM+][BF4-]) IL as a tag, significant enhancement in the MS detection
1183
of the drug in cells was achieved. The ESI-MS sensitivity of the mitoxantrone-IL was an
1184
order of magnitude higher compared to the sensitivity of untagged mitoxantrone.
1185
Additionally, the mitoxantrone-IL was easily identified in the sample containing 53 ACS Paragon Plus Environment
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1186
approximately 100 cells. This strategy has potential to be expanded to other drugs in order to
1187
easily quantify them in small amounts of cells.
1188
To overcome limitations in the low sensitivity of negative ion mode in ESI-MS, paired-ion
1189
electrospray ionization (PIESI) was developed.191,192 In PIESI, adduct formation is exploited
1190
by adding small quantities of polycationic species to form singly-charged complexes with
1191
negative species that can be detected using positive ion mode, greatly enhancing the
1192
sensitivity of the analysis.193
1193
Xu et al. discovered that the structure of the cationic species has significant effects on the
1194
ionization efficiency and sensitivity in ESI-MS.193 The ionization efficiency of a variety of
1195
anionic species was analyzed with either symmetrical or asymmetrical dicationic ILs. By
1196
introducing asymmetry into the dicationic IL structure, similar or lower detection limits were
1197
found for all but one of the studied compounds when compared to using highly symmetrical
1198
cationic species. The authors suggested that the difference in enhancement arises from the
1199
surface active nature of asymmetrical species that is not shared by their symmetrical
1200
counterparts.
1201
Lee et al. used dicationic-based IL pairing reagents for the detection of fatty acids with CE-
1202
MS.194 By using the N,N’-dibutyl 1,1’-pentylenedipyrrolidium-based IL, enhanced
1203
ionization efficiency was observed for the studied fatty acids, particularly short and medium
1204
chained fatty acids. Xu et al. evaluated a series of IL-based ion pairing reagents for the
1205
detection of sphingolipids.195 Up to a 4000-fold enhancement in LODs was observed for
1206
some of the studied analytes when PIESI was used instead of traditional ESI.
1207
Detecting drug metabolites is of significant interest in clinical and forensic applications. Guo
1208
et al. explored PIESI-MS for the detection of glucorinide and sulfate conjugates due to the 54 ACS Paragon Plus Environment
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Analytical Chemistry
1209
fact that their low ionization efficiency in negative ion mode is not ideal for trace level
1210
analysis.196 LODs in the low microgram per liter level were obtained, representing up to a
1211
48-fold improvement with respect to previously reported methods using negative ion mode.
1212
Furthermore, the use of asymmetric pairing reagents resulted in increased sensitivity for over
1213
half of the tested metabolites.
1214
PIESI has also been coupled with the single-probe, a surface microextraction sampling and
1215
ionization device, for MS imaging of biological tissues.197 A wide range of compounds were
1216
identified including adenosine monophosphate, which could not be observed in negative
1217
mode. A total of 1200 metabolites were identified using the dicationic reagent 1,5-
1218
pentanediyl-bis(1-butylpyrrolidinium)
1219
comparison
1220
tripropylphosphonium) fluoride ([C3(P3,3,3,H)22+]2[F-]) IL was used. In another study, the
1221
PIESI-Single probe capabilities were further expanded for single cell analysis.198 Figure 7
1222
shows typical phosphatidylglycerol (PG) mass spectra using traditional ESI-MS (Figure 7a),
1223
and PIESI-MS (Figure 7b and 7c). The formation of the IL-PG complex caused a mass shift
1224
that improved the resolution and resulted in a 28–200 fold improved signal intensity
1225
depending on the IL used as paired ion.
1226
Wang et al. utilized PIESI for the detection of N-blocked amino acids.199 Several polycationic
1227
ILs were studied as paired ions, including dicationic IL-based pyridinium and phosphonium,
1228
and tricationic and tetracationic phosphonium ILs. For the PIESI analysis, the amino acids
1229
were first functionalized with 9-fluorenylmethyl chloroformate. The LODs for the studied
1230
amino acids were 5–100 times lower when using PIESI than when performing the analysis
to
828
metabolites
fluoride identified
([C5(C4Pyr)22+]2[F-]) when
55 ACS Paragon Plus Environment
the
IL
reagent
in
1,5-propanediyl-bis(1-
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1231
by traditional ESI in negative ion mode. Moreover, PIESI was easily compatible with both
1232
linear ion trap and triple quadrupole (QqQ) MS instruments.
1233
Santos et al. used PESI coupled with QqQ MS/MS for the quantification of anionic
1234
surfactants in water.200 Four different dicationic-based ILs containing imidazolium,
1235
phosphonium and pyrrolidinium cations were studied as ion pairing reagents. Among all, the
1236
[C3(P3,3,3,H)22+]2[F-] provided the lowest LODs for the majority of the tested analytes.
1237
Interestingly, similar or higher LODs were achieved using the selected reaction monitoring
1238
and single ion monitoring modes, possibly due to neutral/unknown fragmentation pathways
1239
that reduced the abundance of the monitored ion. The method was coupled with SPE and
1240
applied for the analysis of different water samples. Wastewater was found to contain the
1241
highest amount of anionic surfactants among the analyzed samples.
1242
Matrix effects are well known to be detrimental in analyses performed by LC-ESI-MS, often
1243
hindering quantification and reproducibility. Guo et al. exploited the ion-pairing capabilities
1244
of various dicationic-based ILs for the analysis of four anionic analytes from groundwater
1245
and urine.201 Severe matrix effects were observed when ESI-MS analysis was performed in
1246
the negative SIM mode. However, the addition of ILs significantly reduced the matrix effect
1247
in both of the studied matrixes. When using QqQ as a mass analyzer, slopes that were one to
1248
two orders of magnitude greater than negative ion mode were obtained with PIESI. In
1249
comparison, slopes obtained using a linear ion trap were lower.
1250
PIESI has also been applied for the study of dicamba (3,6-dichloro-2-methoxybenzoic acid)
1251
residues, a broad-spectrum herbicide, from raw agricultural commodities (RACs).202 The
1252
effect of the matrix on the ionization was studied using a post-connector infusion of the
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Analytical Chemistry
1253
standard, which showed minimal effects under the optimized method. Acceptable recoveries
1254
for the three studied analytes were obtained with RSD values ranging from 1-10%.
1255 1256
Electrochemical sensing systems
1257
ILs and PILs have been exploited in the field of electrochemistry for different analytical
1258
purposes due their excellent electrocatalytic properties including high chemical and thermal
1259
stability, high conductivity and wide electrochemical window. In particular, ILs have been
1260
used as electrolytes or as electrode devices in traditional carbon paste electrodes (CPE),
1261
glassy carbon electrodes (GCE) or screen-printed electrodes (ScPE). The main innovations
1262
in this topic within the past several years can be divided into five subsections: ILs as
1263
electrolyte media, IL/carbon-based composite electrochemical sensing systems, IL/metal-
1264
based composite electrochemical sensing systems, IL/hybrid carbon-metal-based composite
1265
electrochemical sensing systems, and biosensors based on ILs.
1266 1267
Ionic liquids as electrolyte media
1268
ILs have been studied in numerous electrochemical applications as electrolyte media due to
1269
their wide electrochemical potential windows compared to traditional electrolytes. These
1270
electrochemical properties, as well as the solubility of the ILs in different media, is highly
1271
dependent on the cation/anion combinations. Abu-Lebdeh et al. designed a new group of
1272
hydrophobic ILs based on amidinium cations.203 The highly-delocalized positive charge and
1273
long alkyl groups of the ILs enabled good miscibility in organic solvents. At the same time,
1274
they presented good ionic conductivities and electrochemical activity, overcoming the
57 ACS Paragon Plus Environment
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1275
limitations of traditional electrolytes which are not soluble in non-polar media. Baldo et al.
1276
reported a new voltammetric/ amperometric method for the determination of oleic acid in
1277
olive oil samples.204 To bypass problems related to the low conductivity of the investigated
1278
samples, the olive oils were mixed with the [P6,6,6,14+][NTf2-] IL, which acted as a supporting
1279
electrolyte. More recently, Rizzo et al. used a dialkyl-1,1′-bibenzimidazolium IL as chiral
1280
additive to provide the enantiodiscrimination of N,N′-dimethyl-1-ferrocenyl-ethylamine in
1281
voltammetry experiments.205
1282
ILs have also allowed for electrochemical studies in non-polar mediums. Mousavi et al.
1283
investigated the electrochemical stabilities of several RTILs based on imidazolium,
1284
pyridinium, pyrrolidinium, piperidinium or quaternary ammonium cations with different
1285
alkyl substituents paired with [NTf2-], [BF4-] or [TfO-] anions.206 The authors found that the
1286
type and size of cation had a major effect on the electrolyte stability, viscosity and
1287
conductivity. Saturated cations with quaternary ammonium substituents generally provided
1288
the highest cathodic stabilities, whereas ILs with aromatic cations were less stable toward
1289
reduction. In addition, ammonium-based ILs offered potential windows much larger than
1290
imidazolium and pyridinium ILs.
1291
Using a unique approach, Joshi et al. reported a non-enzymatic H2O2 sensor.207 This sensor
1292
combined the synergistic effects of catalytically active Pt nanoparticles, the high surface area
1293
of MWCNTs, and the conducting characteristic of the 1-butyl-4-methylpyridinium
1294
hexafluorophosphate ([C4MPy+][PF6-]) IL to achieve high sensitivity for H2O2 oxidation in
1295
saliva samples. The use of IL significantly improved the sensitivity of the sensor by 40%.
1296
Moreover, the pyridinium hexafluorophosphate-based IL showed lower background currents
1297
without any heat pretreatment and was able to achieve lower detection limit. 58 ACS Paragon Plus Environment
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Analytical Chemistry
1298
Ionic liquid/carbon-based composite electrochemical sensing systems
1299
Different carbonaceous materials such as carbon nanotubes (CNTs),208,209 graphene,210-212
1300
and fullerene213 have been combined with ILs to improve the electrochemical properties of
1301
sensing systems. The carbonaceous materials are generally used as CPEs where the ILs are
1302
applied as binders due to their high solvation capacity, substituting for the conventional non-
1303
conductive binding liquids.214,215
1304
Chaiyo et al. prepared a ScPE using a composite consisting of nafion, graphene and 1-butyl-
1305
2,3-dimethylimidazolium tetrafluoroborate ([C4MMIM+][BF4-]) to determine zinc, cadmium
1306
and lead in water simples.216 The presence of the IL in the composite generated well-defined
1307
and enhanced redox peaks, which could be ascribed to the high ionic conductivity of the IL.
1308
Sanati et al. developed an IL/graphene quantum dot modified CPE.212 In this study, the
1309
[C4MIM+][PF6-] IL was used as a binder to increase the electrical conductivity of the
1310
electrode. As a result, good electron mediating behavior and separated oxidation signals of
1311
the analytes were achieved. A study published by Ueda et al. evaluated the electrochemical
1312
properties of fullerene C60 and C70 in ammonium- and pyrrolidinium-based ILs.213 The
1313
authors found that the cation, anion, as well as the chemical structure of the fullerene
1314
influenced the electrochemical band gaps of fullerene. Gomes et al. have developed different
1315
GCEs based on the [C4MIM+][PF6-] IL functionalized with multi-walled carbon nanotubes
1316
(MWCNTs).209 In this application, the electrochemical properties of the GCE were
1317
modulated based on the amount of IL. Therefore, the current signal increased two times for
1318
the MWCNT-[C4MIM+][PF6-]/GCE (1:10) when compared with the [C4MIM+][PF6-]/GCE,
1319
and 1.1 times higher than the MWCNT/GCE. In addition, the MWCNT-[C4MIM+][PF6-
1320
]/GCE presented enhanced electrochemical reactivity compared to the bare GCE, 59 ACS Paragon Plus Environment
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1321
[C4MIM+][PF6-]/GCE and MWCNT/GCE. The high surface energy of the MWCNT was
1322
effectively appeased since they were surrounded by the ILs, providing π-π stacking and
1323
cation-π interactions.
1324 1325
Ionic liquid/metal-based composite electrochemical sensing systems
1326
IL/metal-based composite electrochemical sensing systems are obtained by the combination
1327
of a metal element with ILs and can be applied as CPE, GCE or ScPE. The metal is normally
1328
used either in its oxide form or as nanoparticles. The association of the metal and the IL
1329
contributes a large specific surface area, strong surface reactivity, high conductivity, an
1330
improvement of overpotentials, and an enhancement of response signal in cases where the
1331
composite is used for the fabrication of electrochemical nanosensors or nano-biocomposites.
1332
Gold nanoparticles have been electrodeposited onto the surface of a CPE modified with the
1333
1-butylpyridinium hexafluorophosphate ([C4Py+][PF6-]) IL to immobilize a thyroid
1334
stimulating hormone antibody (anti-TSH).217 In another approach, a CPE modified with CdO
1335
nanoparticles and the [C4MIM+][Br-] IL provided lower oxidation overpotential of vitamin
1336
C and a 5.0-fold increment in the oxidation current studied.218 A sensor constructed using
1337
CuFe2O4 nanoparticles and the 1,3-dipropylimidazolium bromide ([C3C3IM+][Br-]) IL
1338
provided a voltammetric sensor with high sensitivity and electrocatalytic activity.219 The
1339
electronic properties of CuFe2O4 together with the IL promoted charge transfer reactions
1340
when the composite was used as electrode. Regarding its long-term stability, the sensor
1341
response current was able to remain almost constant upon continuous 15 cyclic sweeps over
1342
the applied potential ranging from 0.0 to + 0.60 V and was able to be stored in refrigerator at
1343
4 °C for 30 days. In another study, ZnO and the [C4MIM+][BF4-] IL were added as modifiers 60 ACS Paragon Plus Environment
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Analytical Chemistry
1344
of a CPE, increasing the oxidation current of anticancer drugs.220 This system presented a
1345
sensitivity of 0.0284 μA·μM-1 and 0.0296 μA·μM-1 for doxorubicin and dasatinib,
1346
respectively. Using ZnO nanoparticles combined with the [C6MIM+][PF6-] IL, Karimi-Maleh
1347
et al. constructed a CPE to simultaneously determine isoprenaline and aspirin.221 The
1348
presence of ILs in CPE enhanced the peak currents and decreased the oxidation potential
1349
(decreasing the over potential).
1350 1351
Ionic liquid/hybrid carbonaceous-metal-based composite electrochemical sensing systems
1352
Some published works have been reported in the construction of hybrid systems for the
1353
fabrication of highly sensitive electrochemical sensors. These electrodes bring together the
1354
properties of ILs, metals and carbonaceous materials.
1355
Gold nanoparticles anchored to [C4MIM+][Br-] IL-functionalized GO have been reported for
1356
the determination of dopamine.222 In this system, the IL enhanced the conductivity of the
1357
electrode by preventing the agglomeration of GO. In another application, Cheraghi et al.
1358
described a CPE modified with cadmium oxide nanoparticles decorated with SWCNT
1359
(CdO/SWCNTs) and the [C3C3IM+][Br-] IL as binder between the two components.223 The
1360
developed CPE significantly enhanced the electro-oxidation signal of vanillin in food
1361
samples. Moreover, with this modification the sensitivity increased by ∼5 times with a ∼85
1362
mV reduction in overvoltage. In another study, a nanocomposite consisting of platinum-
1363
tungsten alloy nanoparticles, sheets of reduced GO and the [C4MIM+][Cl-] IL were deposited
1364
onto the surface of a GCE.224 The modified GCE exhibited excellent electrocatalytic activity
1365
towards the oxidation of NO with a strong peak at 0.78 V versus Ag/AgCl due to the
1366
synergistic effects of the electrode components. Damiri et al. described the development of 61 ACS Paragon Plus Environment
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1367
a CPE modified with [C4MIM+][Cl-]/cobalt hexacyanoferrate nanoparticles.225 The presence
1368
of both cobalt hexacyanoferrate nanoparticles and the IL caused a decrease of the
1369
overpotential for the anodic oxidation of diclofenac and an increase in the rate of
1370
heterogeneous electron transfer.
1371
Other different IL/metal/carbonaceous material composites used as electrochemical systems
1372
include IL/cobalt nanoparticles/CNTs226 and IL/MgO/CNTs.227
1373 1374
Biosensors based on ionic liquids
1375
The electrochemical analysis of different compounds in biological samples is a major
1376
challenge. This is largely because target analytes are normally present at trace levels, and the
1377
matrix often contains endogenous compounds such as proteins, lipids, ions, and water that
1378
may interfere in the measurements. However, developments made in this area by combining
1379
ILs with different carbonaceous materials, metal or oxide nanoparticles in the traditional
1380
CPE, GCE, ScPE have improved the electrochemical response of these biosensors, allowing
1381
their application in complex matrices such as plasma, urine, tissues, blood, serum, and saliva.
1382
Table 3 summarizes a number of important examples that have employed IL-modified
1383
biosensors in numerous applications.208,210-212,217,219-221,224-238
1384
The 1-butyl-1-methylpiperidinium hexafluorophosphate ([C4MPip+][PF6-]) IL was applied in
1385
a GO/CD GCE to determine neurotransmitters in human urine samples.228 This electrode
1386
possessed good electron mobility, large surface area, and high ionic conductivity and
1387
stability. A hybrid IL/PtPd alloy nanoparticles/functionalized graphene paper electrode was
1388
fabricated and exhibited high selectivity and sensitivity in bio-catalytic processes and in real-
62 ACS Paragon Plus Environment
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Analytical Chemistry
1389
time tracking of hydrogen peroxide secretion by living human cells.239 The live cells
1390
maintained ∼90% viability after 4 h incubation using this electrochemical device, indicating
1391
that the hybrid electrodes possess high biocompatibility. El-Hady et al. reported two novel
1392
sensors based on human serum albumin (HSA)/IL and BSA/IL composites.229 These GCEs
1393
were used for the determination of vitamins B2, B6 and C in human plasma using analyte
1394
focusing by ionic liquid micelle collapse (AFMC). In this study, the [C8MIM+][PF6-] IL was
1395
used to prepare the electrode. An enhancement in vitamin stability was observed when this
1396
IL was used in the electrode above its critical micelle concentration due to the formation of
1397
complexes with IL micelles. An antibody–antigen based impedimetric immunosensor was
1398
fabricated by the immobilization of monoclonal HER2 antibody on a CPE composite based
1399
on gold nanoparticles/[C2MIM+][PF6-]/CNTs.230 The high conductivity of the IL significantly
1400
enhanced the sensitivity of the immunosensor, which was applied for low level detection of
1401
HER2 in serum samples of breast cancer patients. Another example of an electrochemical
1402
immunosensor was reported by Mazloum-Ardakani et al.234 In this study, a composite based
1403
on [C4MIM+][NTf2-]/fullerene-functionalized MWCNTs/antibody was successfully applied
1404
for detection of tumor necrosis factor α in serum samples for protein diagnostics and
1405
bioassays. The use of the IL promoted a more uniform composite film. In another approach,
1406
the [C4MIM+][PF6-] IL was used to modify the surface of a ScPE for the further
1407
electrodeposition of gold nanoparticles.235 The specific antibody for the electrochemical
1408
detection of Salmonella pullorum and Salmonella gallinaru was immobilized on gold
1409
nanoparticles. This IL-based bionsensor was compared with an analogous sensor based β-
1410
CB, sodium alginate, and chitosan. Among these four different modified electrodes, the
1411
activity of the antibody against bacteria was highest under IL modified conditions. In this
1412
case, the IL provided a friendly microenvironment for proteins while maintaining the 63 ACS Paragon Plus Environment
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1413
biological activity of the antibody and enzyme. An IL/quantum dot fluorescence sensing
1414
array system was reported by Chen et al. for the discrimination of 8 proteins at 500 mmol·L-1
1415
in urine samples.240 The prepared IL/quantum dot conjugate was mixed with the sample
1416
containing the proteins, and fluorescence measurements were used for their determination.
1417
Among the different ILs, the [C4MIM+][Br-] IL provided the highest fluorescence.
1418
Molecularly imprinted polymer (MIP) electrochemical sensors exhibit high selectivity to
1419
determine analytes in complex matrixes. These materials possess specific molecular cavities
1420
that can mimic the shape of the target molecule, resulting in a surface with complementary
1421
chemical functionality to the target molecule.236 When ILs or PILs are used to prepare MIPs,
1422
the imprinted IL-polymer shows fast rebinding rates and high adsorption capacity for the
1423
target analyte.238 The 1,3-di(3-N-pyrrol-propyl)imidazolium bromide ([(PyrC3)2IM+][Br-])
1424
IL and neuron specific enolase were used as functional monomer and template, respectively,
1425
to fabricate an IL-MIP sensor. This sensor was able to determine neuronspecific enolase in
1426
the presence of human serum albumin, human immunoglobulin, hemoglobin, glycine, L-
1427
cysteine, L-histidine, and ascorbic acid at 0.1 ng mL-1. Additional IL-MIP modified based
1428
sensors were reported to determine diclofenac225 and ractopamine237 in urine samples. Wang
1429
et al. fabricated a MIP-hydrogel for the determination of Epididymis Protein 4 (HE4).241 The
1430
IL contained special moieties (amino, carboxyl groups, and the imidazolium cation) that
1431
resulted in active sites to interact with Epididymis HE4 by hydrogen bonding and
1432
electrostatic attractions, which enhanced the selectivity of the imprinted sensor. A MIP-
1433
electrochemical sensor was reported to recognize large molecules such bovine serum
1434
albumin.238 The authors used a reaction mixture consisting of 3-(3-aminopropyl)-1-
1435
vinylimidazolium tetrafluoroborate as functional monomer, N, N′-methylenebisacrylamide
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Analytical Chemistry
1436
as crosslinker, ammonium persulfate and N,N,N′,N′-tetramethylethylenediamine as
1437
initiators, and BSA as template to produce the polymer. The synthesis was carried out in the
1438
presence of carboxyl functionalized MWCNTs, which acted as a support to coat the MIP.
1439 1440
Conclusions and perspective
1441
The unique features of ILs and corresponding derivatives continue to be exploited in many
1442
ways within all of the major fields of analytical chemistry. In sample preparation, ILs have
1443
been effectively used as solvents in liquid-phase (micro)extraction and as customizable
1444
sorbent materials in solid-phase (micro)extraction. In these applications, ILs often have been
1445
shown to exhibit better extraction performance than conventional solvents or commercially-
1446
available sorbent materials. TSILs, such as choline amino acids, have continued to show
1447
remarkable selectivity when used as extraction solvents. Over the last several years, studies
1448
demonstrating the use of MILs in a variety of platforms have increased dramatically and are
1449
expected to increase as fundamental studies provide insight into their ordering in magnetic
1450
fields. Additionally, it is expected that more efficient synthetic methods will continue to be
1451
reported describing the preparation of low viscosity solvents with high magnetic
1452
susceptibility.
1453
In chemical separations, ILs continue to be explored as unique selectivity stationary phases
1454
in one and two-dimensional GC. Continual efforts in further understanding the
1455
decomposition/volatilization of IL and PIL-based stationary phases is needed to assist in the
1456
design of more thermally-stable compounds. In HPLC and CE separations, ILs exhibit unique
1457
features that make them interesting additives and chiral selectors in chiral separations. An
1458
understanding of how ILs order on the nanoscale will further advance the field of separations 65 ACS Paragon Plus Environment
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1459
science. In mass spectrometry, IL-based matrixes continue to be explored in MALDI-MS to
1460
enhance the ionization of large molecules, and as additives in PIESI-MS for increasing the
1461
sensitivity of the traditional ESI-MS in negative ion mode. New approaches that are capable
1462
of merging sample preparation with MALDI-MS using IL-based solvents/matrixes offer
1463
promise in decreasing sample preparation time and complexity.
1464
ILs have been also employed for the development of different electrodes, including CPE,
1465
GCE or ScPE. In particular, ILs have been added in carbonaceous, metal or hybrid
1466
composites for the development of a wide variety of electrochemical sensors and biosensors.
1467
Many of these studies have exploited the chemical tunability of ILs to design conductive
1468
solvents that can be incorporated into the function of the electrode. ILs will undoubtedly
1469
continue to be highly studied in electroanalytical chemistry, particularly in areas where their
1470
unique features can be exploited in chip-based platforms. Finally, this critical review
1471
highlights the numerous advances that ILs have made in biomolecule analysis, which has
1472
increased significantly over the past several years. As they continue to be explored in
1473
bioanalytical applications, IL solvents that are greener alternatives should be investigated.
66 ACS Paragon Plus Environment
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Analytical Chemistry
Author information Corresponding author
1476
Department of Chemistry, Iowa State University, 1605 Gilman Hall, Ames, IA, 50011, USA,
1477
E-mail:
[email protected] 1478
Notes
1479
Biographies
1480
Jared L. Anderson is a Professor of Chemistry at Iowa State University. His research
1481
focuses on the development of stationary phases for multidimensional chromatography,
1482
alternative approaches for sample preparation, particularly in nucleic acid isolation and
1483
purification, and developing analytical tools for trace-level analysis within active
1484
pharmaceutical ingredients.
1485
María J. Trujillo-Rodríguez obtained her B.S. degree in chemistry in 2012, M.S. in
1486
research in chemistry in 2013 and Ph.D. in chemistry in 2017 in Universidad de La Laguna,
1487
Spain. She has worked as Postdoctoral Research Associate in Professor Anderson’s research
1488
group in Iowa State University since 2017. Her research interests include the development
1489
of new microextraction procedures using ionic liquids and derivatives for environmental and
1490
food analysis.
1491
He Nan completed his B.S. degree in chemistry at Heilongjiang University in China and
1492
M.S. degree in analytical chemistry at Kyung Hee University in Korea. He is currently a
1493
Ph.D. student in the Department of Chemistry at Iowa State University working under the
1494
supervision of Professor Anderson. His research focuses on developing new sample
67 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1495
preparation methods, new stationary phases in chromatographic separations, and using
1496
comprehensive two-dimensional gas chromatography in the resolution of complex samples.
1497
Marcelino O. Varona obtained his B.S. degree in chemistry and biology at Concordia
1498
University in 2016. He is currently a Ph.D. student in the Department of Chemistry at Iowa
1499
State University working under the supervision of Professor Anderson. His research focuses
1500
on the use of polymeric ionic liquids and solid-phase microextraction for bioanalytical
1501
applications.
1502
Miranda N. Emaus obtained her B.S. degree in chemistry and forensic chemistry at Lake
1503
Superior State University in 2016. She is currently a Ph.D. student in the Department of
1504
Chemistry at Iowa State University working under the supervision of Professor Anderson.
1505
Her research involves the use of magnetic ionic liquid for achieving sequence selective DNA
1506
extraction.
1507
Israel D. Souza received his B.S. and M.S. degree at University of Sao Paulo, Brazil, in 2013
1508
and 2015, respectively. He is currently a Ph.D. student at University of Sao Paulo working
1509
under Professor Maria Eugênia Queiroz; in 2018, he spent 6 months as a visiting Ph.D.
1510
student at Iowa State University in the laboratory of Professor Anderson. His research
1511
focuses on development of selective and innovative materials including ionic liquids,
1512
polymeric ionic liquids, molecularly imprinted polymer, and restricted access materials to
1513
apply as stationary phases in gas chromatography and as sorbents in microextraction
1514
techniques.
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References (1) Lei, Z.; Chen, B.; Koo, Y. -M.; MacFarlane, D. R. Chem. Rev. 2017, 117, 6633– 6635. (2) Ho, T. D.; Zhang, C.; Hantao, L. W.; Anderson, J. L. Anal. Chem. 2014, 86, 262– 285. (3) H. Davis, Jr., J. Chem. Lett. 2004, 33, 1072–1077. (4) Mecerreyes, D. Prog. Polym. Sci. 2011, 36, 1629–1648. (5) Yuan, J.; Mecerreyes, D.; Antonietti, M. Prog. Polym. Sci. 2013, 38, 1009–1036. (6) Clark, K. D.; Nacham, O.; Purslow, J. A.; Pierson, S. A.; Anderson, J. L. Anal. Chim. Acta 2016, 934, 9–21. (7) Clark, K. D.; Emaus, M. N.; Varona, M.; Bowers, A. N.; Anderson, J. L. J. Sep. Sci. 2018, 41, 209–235. (8) Nawała, J.; Dawidziuk, B.; Dziedzic, D.; Gordon, D.; Popiel, S. Trac - Trends Anal. Chem. 2018, 105, 18–36. (9) An, J.; Trujillo-Rodríguez, M. J.; Pino, V.; Anderson, J. L. J. Chromatogr. A 2017, 1500, 1–23. (10) Trujillo-Rodríguez, M. J.; Rocío-Bautista, P.; Pino, V.; Afonso, A. Trac - Trends Anal. Chem. 2013, 51, 87–106. (11) Shukla, S. K.; Pandey, S.; Pandey, S. J. Chromatogr. A 2018, 1559, 44–61. (12) Berthod, A.; Ruiz-Ángel, M. J.; Carda-Broch, S. J. Chromatogr. A 2018, 1559, 2– 16. (13) Fanali, C.; Micalizzi, G.; Dugo, P.; Mondello, L. Analyst 2017, 142, 4601–4612. (14) Nan, H.; Anderson, J. L. Trac - Trends Anal. Chem. 2018, 105, 367–379. (15) Greño, M.; Marina, M. L.; Castro-Puyana, M. Crit. Rev. Anal. Chem. 2018, 48, 429– 446. (16) Abdelhamid, H. N. Organic Matrices, Trac - Trends Anal. Chem. 2017, 89, 68–98. (17) Wang, X.; Hao, J. Sci. Bull. 2016, 61, 1281–1295. (18) Clark, K. D.; Trujillo-Rodríguez, M. J.; Anderson, J. L. Anal. Bioanal. Chem. 2018, 410, 4567–4573. (19) Wang, X.; Akhmedov, N. G.; Duan, Y.; Luebke, D.; Hopkinson, D.; Li, B. ACS Appl. Mater. Interfaces 2013, 5, 8670–8677. (20) Tokalıoğlu, Ş.; Yavuz, E.; Şahan, H.; Gökhan Çolak, S.; Ocakoğlu, K.; Kaçer, M.; Patat, Ş. Talanta. 2016, 159, 222–230. (21) Wang, H.; Liu, C.; Huang, X.; Jia, C.; Cao, Y.; Hu, L.; Lu, R.; Zhang, S.; Gao, H.; Zhou, W.; Xu, D. New J. Chem. 2018, 42, 8791–8799. (22) Zhang, W.; Feng, X.; Alula, Y.; Yao, S. Food Chem. 2017, 230, 637–648. (23) Zhang, H.; Wu, X.; Yuan, Y.; Han, D.; Qiao, F.; Yan, H. Food Chem. 2018, 265, 290–297. (24) Han, Y.; Yang, C.; Zhou, Y.; Han, D.; Yan, H. J. Agric. Food Chem. 2017, 65, 1750–1757. (25) Ferreira, D. C.; de Toffoli, A. L.; Maciel, E. V. S.; Lanças, F. M. Electrophoresis 69 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1556 1557 1558
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1559 1560
(27)
1561 1562
(28)
1563 1564
(29)
1565 1566
(30)
1567
(31) (32)
1568 1569 1570 1571
(33)
1572
(34) (35)
1573 1574 1575 1576 1577 1578 1579 1580 1581
(36) (37) (38) (39) (40)
1582 1583
(41)
1584 1585
(42)
1586 1587
(43)
1588 1589 1590
(44)
1591
(45) (46) (47) (48) (49) (50)
1592 1593 1594 1595 1596
2018, 39, 2210–2217. Wang, X.; Xing, L.; Shu, Y.; Chen, X.; Wang, J. Anal. Chim. Acta 2014, 837, 64– 69. Dang, M.; Deng, Q.; Fang, G.; Zhang, D.; Liu, J.; Wang, S. J. Mater. Chem. B 2017, 5, 6339–6347. Dai, X.; Wang, D.; Li, H.; Chen, Y.; Gong, Z.; Xiang, H.; Shi, S.; Chen, X. J. Chromatogr. A 2017, 1484, 7–13. Liu, S.; Wang, C.; Shuai, H.; Ligai, B.; Liu, H. Chromatographia 2016, 79, 441– 449. Pang, X.; Bai, L.; Lan, D.; Guo, B.; Wang, H.; Liu, H.; Ma, Z. Chromatographia 2018, 81, 1391–1400. Shi, F.; Liu, J.; Liang, K.; Liu, R. J. Chromatogr. A 2016, 1447, 9–16. Pang, L.; Pang, R.; Ge, L.; Zheng, L.; Zhao, J.; Zhang, H. J. Sep. Sci. 2016, 39 , 4415–4421. Pacheco-Fernández, I.; Najafi, A.; Pino, V.; Anderson, J. L.; Ayala, J. H.; Afonso, A. M. Talanta 2016, 158, 125–133. An, J.; Anderson, J. L. Talanta 2018, 182, 74–82. Trujillo-Rodríguez, M. J.; Nan, H.; Anderson, J. L. J. Chromatogr. A 2018, 1540, 11–20. Sun, M.; Bu, Y.; Feng, J.; Luo, C. J. Sep. Sci. 2016, 39, 375–382. Liao, K.; Mei, M.; Li, H.; Huang, X.; Wu, C. J. Sep. Sci. 2016, 39, 566–575. Pei, M.; Zhang, Z.; Huang, X.; Wu, Y. Talanta 2017, 165, 152–160. Trujillo-Rodríguez, M. J.; Anderson, J. L. Anal. Chim. Acta 2018, in press, DOI: 10.1016/j.aca.2018.09.051 Cagliero, C.; Ho, T. D.; Zhang, C.; Bicchi, C.; Anderson, J. L. J. Chromatogr. A 2016, 1449, 2–7. Cagliero, C.; Nan, H.; Bicchi, C.; Anderson, J. L. J. Chromatogr. A 2016, 1459, 17– 23. Hou, X.; Guo, Y.; Liang, X.; Wang, X.; Wang, L.; Wang, L.; Liu, X. Talanta 2016, 153, 392–400. Gionfriddo, E.; Souza-Silva, É. A.; Ho, T. D.; Anderson, J. L.; Pawliszyn, J. Talanta 2018, 188, 522–530. Crucello, J.; Miron, L. F. O.; Ferreira, V. H. C.; Nan, H.; Marques, M. O. M.; Ritschel, P. S.; Zanus, M. C.; Anderson, J. L.; Poppi, R. J.; Hantao, L. W. Anal. Bioanal. Chem. 2018, 410, 4749–4762. Sun, M.; Feng, J.; Bu, Y.; Luo, C. J. Chromatogr. A 2016, 1458, 1–8. Feng, J.; Wang, X.; Tian, Y.; Luo, C.; Sun, M. J. Sep. Sci. 2018, 41, 3267–3274. Wu, M.; Wang, L.; Zeng, B.; Zhao, F. J. Chromatogr. A 2016, 1444, 42–49. Ai, Y.; Wu, M.; Li, L.; Zhao, F.; Zeng, B. J. Chromatogr. A 2016, 1437, 1–7. Feng, Y.; Wu, M.; Zhao, F.; Zeng, B. Talanta 2016, 148, 356–361. Tang, Z.; Duan, Y. Talanta 2017, 172, 45–52. 70 ACS Paragon Plus Environment
Page 70 of 99
Page 71 of 99 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
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1599 1600
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(54) (55)
1604 1605 1606 1607
(56)
1608 1609
(57)
1610
(58) (59)
1611 1612 1613 1614 1615
(60) (61)
1616 1617
(62)
1618 1619
(63)
1620 1621
(64)
1622 1623
(65)
1624 1625
(66)
1626
(67) (68)
1627 1628 1629 1630
(69)
1631 1632
(70)
1633 1634
(71)
1635 1636
(72)
1637
(73) (74)
1638
Souza, I. D.; Hantao, L. W.; Eug, M.; Queiroz, C. Anal. Chim. Acta 2018, in press, DOI: 10.1016/j.aca.2018.08.062. Young, J. A.; Zhang, C.; Devasurendra, A. M.; Tillekeratne, L. M. V.; Anderson, J. L.; Kirchhoff, J. R. Anal. Chim. Acta 2016, 910, 45–52. Devasurendra, A. M.; Zhang, C.; Young, J. A.; Tillekeratne, L. M. V.; Anderson, J. L.; Kirchhoff, J. R. ACS Appl. Mater. Interfaces 2017, 9, 24955–24963. Nacham, O.; Clark, K. D.; Anderson, J. L. Anal. Chem. 2016, 88, 7813–7820. Nacham, O.; Clark, K. D.; Varona, M.; Anderson, J. L. Anal. Chem. 2017, 89, 10661–10666. Varona, M.; Ding, X.; Clark, K. D.; Anderson, J. L. Anal. Chem. 2018, 90, 6922– 6928. Cacho, J. I.; Campillo, N.; Viñas, P.; Hernández-Córdoba, M. Anal. Bioanal. Chem. 2016, 408, 243–249. Wang, L.; Zhang, D.; Xu, X.; Zhang, L. Food Chem. 2016, 197, 754–760. Wang, H.; Hu, L.; Li, W.; Lu, R.; Zhang, S.; Zhou, W.; Gao, H. J. Chromatogr. A 2016, 1471, 60–67. Suárez, R.; Clavijo, S.; Avivar, J.; Cerdà, V. Talanta 2016, 148, 589–595. Zhang, C.; Cagliero, C.; Pierson, S. A.; Anderson, J. L. J. Chromatogr. A 2016, 1481, 1–11. Yang, M.; Wu, X.; Jia, Y.; Xi, X.; Yang, X.; Lu, R.; Zhang, S.; Gao, H.; Zhou, W. Anal. Chim. Acta 2016, 906, 118–127. Akhond, M.; Absalan, G.; Pourshamsi, T.; Ramezani, A. M. Talanta 2016, 154, 461–466. De Boeck, M.; Dubrulle, L.; Dehaen, W.; Tytgat, J.; Cuypers, E. Talanta 2018, 180, 292–299. Wang, H.; Gao, J.; Yu, N.; Qu, J.; Fang, F.; Wang, H.; Wang, M.; Wang, X. Talanta 2016, 154, 381–391. Pacheco-Fernández, I.; Pino, V.; Lorenzo-Morales, J.; Ayala, J. H.; Afonso, A. M. Anal. Bioanal. Chem. 2018, 410, 4701–4713. Shirkhanloo, H.; Ghazaghi, M.; Mousavi, H. Z. J. Mol. Liq. 2016, 218, 478–483. Fernández, E.; Vidal, L.; Costa-García, A.; Canals, A. Anal. Chim. Acta 2016, 915, 49–55. Arain, S. A.; Kazi, T. G.; Afridi, H. I.; Arain, M. S.; Panhwar, A. H.; Khan, N.; Baig, J. A.; Shah, F. Ecotoxicol. Environ. Saf. 2016, 126, 186–192. Nacham, O.; Clark, K. D.; Yu, H.; Anderson, J. L. Chem. Mater. 2015, 27, 923– 931. Pierson, S. A.; Nacham, O.; Clark, K. D.; Nan, H.; Mudryk, Y.; Anderson, J. L. New J. Chem. 2017, 41, 5498–5505. Trujillo-Rodríguez, M. J.; Nacham, O.; Clark, K. D.; Pino, V.; Anderson, J. L.; Ayala, J. H.; Afonso, A. M. Anal. Chim. Acta 2016, 934, 106–113. Yu, H.; Merib, J.; Anderson, J. L. J. Chromatogr. A 2016, 1463, 11–19. Chisvert, A.; Benedé, J. L.; Anderson, J. L.; Pierson, S. A.; Salvador, Anal. Chim. 71 ACS Paragon Plus Environment
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1639 1640 1641
(75)
1642 1643
(76)
1644 1645
(77)
1646 1647
(78)
1648
(79) (80)
1649 1650 1651 1652
(81)
1653
(82) (83) (84) (85)
1654 1655 1656 1657 1658 1659
(86)
1660
(87) (88)
1661 1662 1663 1664
(89)
1665 1666
(90)
1667 1668
(91)
1669 1670
(92)
1671
(93) (94)
1672 1673 1674 1675 1676 1677 1678 1679
(95) (96) (97) (98)
Acta 2017, 983, 130–140. Clark, K. D.; Varona, M.; Anderson, J. L. Angew. Chem. - Int. Ed. 2017, 56, 7630– 7633. Peng, X.; Clark, K. D.; Ding, X.; Zhu, C.; Varona, M.; Emaus, M. N.; An, J.; Anderson, J. L. Chem. Commun. 2018, 54, 10284–10287. Clark, K. D.; Purslow, J. A.; Pierson, S. A.; Nacham, O.; Anderson, J. L. Anal. Bioanal. Chem. 2017, 409, 4983–4991. Merib, J.; Spudeit, D. A.; Corazza, G.; Carasek, E.; Anderson, J. L. Anal. Bioanal. Chem. 2018, 410, 4689–4699. An, J.; Rahn, K. L.; Anderson, J. L. Talanta 2017, 167, 268–278. Emaus, M. N.; Clark, K. D.; Hinners, P.; Anderson, J. L. Anal. Bioanal. Chem. 2018, 410, 4135–4144. Ding, X.; Clark, K. D.; Varona, M.; Emaus, M. N.; Anderson, J. L. Anal. Chim. Acta, 2018, in press, DOI: 10.1016/j.aca.2018.09.014. Trujillo-Rodríguez, M. J.; Pino, V.; Anderson, J. L. Talanta 2017, 172, 86–94. Fernández, E.; Vidal, L.; Canals, A. Anal. Bioanal. Chem. 2018, 410, 4679–4687. Yao, T.; Yao, S. J. Chromatogr. A 2017, 1481, 12–22. Hsu, K. C.; Lee, C. F.; Chao, Y. Y.; Hung, C. C.; Chen, P. C.; Chiang, C. H.; Huang, Y. L. J. Anal. At. Spectrom. 2016, 31, 2338–2345. López-López, J. A.; Pirkwieser, P.; Leyma, R.; Kandioller, W.; Krachler, R.; Keppler, B. K.; Jirsa, F.; Moreno, C. J. Clean. Prod. 2018, 201, 22–27. Wang, J.; Huang, S.; Wang, P.; Yang, Y. Food Control 2016, 67, 278–284. Xu, H.; Mi, H. Y.; Guan, M. M.; Shan, H. Y.; Fei, Q.; Huan, Y. F.; Zhang, Z. Q.; Feng, G. D. Food Chem. 2017, 232, 198–202. Pimparu, R.; Nitiyanontakit, S.; Miró, M.; Varanusupakul, P. Talanta 2016, 161, 730–734. Alahmad, W.; Tungkijanansin, N.; Kaneta, T.; Varanusupakul, P. Talanta 2018, 190, 78–84. Freire, M. G.; Cláudio, A. F. M.; Araújo, J. M. M.; Coutinho, J. A. P.; Marrucho, I. M.; Lopes, J. N. C.; Rebelo, L. P. N. Chem. Soc. Rev. 2012, 41, 4966–4995. Sousa, R. de C. S.; Pereira, M. M.; Freire, M. G.; Coutinho, J. A. P. Sep. Purif. Technol. 2018, 196, 244–253. Chakraborty, A.; Sen, K. J. Chromatogr. A 2016, 1433, 41–55. Gras, M.; Papaiconomou, N.; Schaeffer, N.; Chainet, E.; Tedjar, F.; Coutinho, J. A. P.; Billard, I. Angew. Chem. - Int. Ed. 2018, 57, 1563–1566. Chen, Y.; Wang, H.; Pei, Y.; Wang, J. Talanta 2018, 182, 450–455. Sadeghi, S.; Moghaddam, A. Z. J. Mol. Liq. 2016, 221, 798–804. Dimitrijević, A.; Ignjatović, L.; Tot, A.; Vraneš, M.; Zec, N.; Gadžurić, S.; TrtićPetrović, T. J. Mol. Liq. 2017, 243, 646–653. Almeida, H. F. D.; Freire, M. G.; Marrucho, I. M. Green Chem. 2016, 18, 2717– 2725. 72 ACS Paragon Plus Environment
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1719 1720
(123)
Ferreira, A. M.; Cláudio, A. F. M.; Válega, M.; Domingues, F. M. J.; Silvestre, A. J. D.; Rogers, R. D.; Coutinho, J. A. P.; Freire, M. G. Green Chem. 2017, 19, 2768– 2773. Quental, M. V.; Pereira, M. M.; Ferreira, A. M.; Pedro, S. N.; Shahriari, S.; Mohamadou, A.; Coutinho, J. A. P.; Freire, M. G. Green Chem. 2018, 20, 2978– 2983. Bogdanov, M. G.; Svinyarov, I. J. Chromatogr. A 2018, 1559, 62–68. Zawadzki, M.; e Silva, F. A.; Domańska, U.; Coutinho, J. A. P.; Ventura, S. P. M. Green Chem. 2016, 18, 3527–3536. Yang, H.; Chen, L.; Zhou, C.; Yu, X.; Yagoub, A. E. G. A.; Ma, H. Food Chem. 2018, 245, 346–352. Marchel, M.; João, K. G.; Marrucho, I. M. Sep. Purif. Technol. 2018, 210, 710–718. Gupta, B. S.; Taha, M.; Lee, M. J. RSC Adv. 2016, 6, 18567–18576. Mondal, D.; Sharma, M.; Quental, M. V.; Tavares, A. P. M.; Prasad, K.; Freire, M. G. Green Chem. 2016, 18, 6071–6081. Armstrong, D. W.; He, L. F.; Liu, Y. S. Anal. Chem. 1999, 71, 3873–3876. Poole, C. F.; Lenca, N. J. Chromatogr. A 2014, 1357, 87–109. Yao, C.; Anderson, J. L. J. Chromatogr. A 2009, 1216, 1658–1712. Ragonese, C.; Sciarrone, D.; Tranchida, P. Q.; Dugo, P.; Dugo, G.; Mondello, L. Anal. Chem. 2011, 83, 7947–7954. Lenca, N.; Poole, C. F. J. Chromatogr. A 2017, 1525, 138–144. Lenca, N.; Poole, C. F. J. Chromatogr. A 2017, 1524, 210–214. Lenca, N.; Poole, C. F. J. Chromatogr. A 2018, 1559, 164–169. Patil, R. A.; Talebi, M.; Berthod, A.; Armstrong, D. W. Anal. Bioanal. Chem. 2018, 410, 4645–4655. Anderson, J. L.; Ding, R.; Ellern, A.; Armstrong, D. W. J. Am. Chem. Soc. 2005, 127, 593–604. Maton, C.; De Vos, N.; Stevens, C. V. Chem. Soc. Rev. 2013, 42, 5963–5977. Hantao, L. W.; Najafi, A.; Zhang, C.; Augusto, F.; Anderson, J. L. Anal. Chem. 2014, 86, 3717–3721. Regmi, B. P.; Chan, R.; Agah, M. J. Chromatogr. A 2017, 1510, 66–72. Pello-Palma, J.; Gonzalez-Alvarez, J.; Gutierrez-Alvarez, M. D.; Dapena de la Fuente, E.; Mangas-Alonso, J. J.; Mendez-Sanchez, D.; Gotor-Fernandez, V.; AriasAbrodo, P. Anal. Bioanal. Chem. 2017, 409, 3033–3041. Dai, J.-L.; Zhao, L.-H.; Shi, J.-H. J. Sep. Sci. 2017, 40, 2769–2778. Nan, H.; Zhang, C.; O’Brien, R. A.; Benchea, A.; Davis Jr, J. H.; Anderson, J. L. J. Chromatogr. A 2017, 1481, 127–136. Patil, R. A.; Talebi, M.; Sidisky, L. M.; Armstrong, D. W. Chromatographia 2017, 80, 1563–1574. Talebi, M.; Patil, R. A.; Sidisky, L. M.; Berthod, A.; Armstrong, D. W. Anal. Bioanal. Chem. 2017, 410, 4633–4643. 73 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1721 1722 1723 1724
(124) (125) (126)
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(128) (129) (130) (131) (132)
1728 1729 1730 1731 1732 1733 1734 1735 1736 1737 1738 1739 1740 1741 1742
(133) (134) (135) (136) (137) (138) (139) (140)
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(142)
1747 1748
(143)
1749 1750
(144)
1751
(145) (146) (147)
1752 1753 1754 1755 1756
(148)
1757 1758
(149)
1759 1760
(150)
Talebi, M.; Patil, R. A.; Armstrong, D. W. J. Mol. Liq. 2018, 256, 247–255. Jiang, R.; Liu, T.; Yang, S.; Sun, L.; Luo, A. Acta Chromatogr. 2017, 29, 25–43. Heydar, K. T.; Azadeh, A. M.; Yaghoubnejad, S.; Ghonouei, N.; Sharifi, A.; Rahnama, M. A. J. Chromatogr. A 2017, 1511, 92–100. Talebi, M.; Patil, R. A.; Sidisky, L. M.; Berthod, A.; Armstrong, D. W. Anal. Chim. Acta 2018, in press, DOI: 10.1016/j.aca.2018.07.047. Shashkov, M. V.; Sidelnikov, V. N. J. Sep. Sci. 2016, 39, 3754–3760. Roeleveld, K.; David, F.; Lynen, F. J. Chromatogr. A 2016, 1451, 135–144. Zhang, C.; Park, R. A.; Anderson, J. L. J. Chromatogr. A 2016, 1440, 160–171. Gil-Av, E.; Herling, J.; Shabtai, J. J. Chromatogr. 1958, 1, 508–512. Rodinkov, O. V.; Zhuravleva, G. A.; Moskvin, L. N. J. Anal. Chem. 2016, 71, 1046– 1051. Wasiak, W.; Rykowska, I. J. Chromatogr. A 1997, 773, 209–217. Wawrzyniak, R.; Wasiak, W. Analytica Chimica Acta 1998, 377, 61–70. Nan, H.; Zhang, C.; Venkatesh, A.; Rossini, A. J.; Anderson, J. L. J. Chromatogr. A 2017, 1523, 316–320. Nan, H.; Peterson, L.; Anderson, J. L. Anal. Bioanal. Chem. 2017, 410, 4597–4606. Frink, L. A.; Armstrong, D. W. Anal. Chem. 2016, 88, 8194–8201. Frink, L. A.; Armstrong, D. W. Food Chem. 2016, 205, 23–27. Frink, L. A.; Armstrong, D. W. J. Pharm. Sci. 2016, 105, 2288–2292. Cagliero, C.; Bicchi, C.; Cordero, C.; Liberto, E.; Rubiolo, P.; Sgorbini, B. Anal. Bioanal. Chem. 2018, 410, 4657–4668. Amaral, M. S. S.; Marriott, P. J.; Bizzo, H. R.; Rezende, C. M. Anal. Bioanal. Chem. 2017, 410, 4615–4632. Cagliero, C.; Bicchi, C.; Cordero, C.; Liberto, E.; Rubiolo, P.; Sgorbini, B. J. Chromatogr. A 2017, 1495, 64–75. Pojjanapornpun, S.; Nolvachai, Y.; Aryusuk, K.; Kulsing, C.; Krisnangkura, K.; Marriott, P. J. Anal. Bioanal. Chem. 2018, 410, 4669–4677. Gómez-Cortés, P.; Rodriguez-Pino, V.; Juarez, M.; de la Fuente, M. A. Food Chem. 2017, 231, 11–18. Nolvachai, Y.; Kulsing, C.; Marriott, P. J. Anal. Chem. 2015, 87, 538–544. Delmonte, P. J. Chromatogr. A 2016, 1460, 160–172. Webster, R. L.; Rawson, P. M.; Evans, D. J.; Marriott, P. J. J. Sep. Sci. 2016, 39, 2537–2543. Sciarrone, D.; Schepis, A.; Zoccali, M.; Donato, P.; Vita, F.; Creti, D.; Alpi, A.; Mondello, L. Anal. Chem. 2018, 90, 6610–6617. Ros, M.; Escobar-Arnanz, J.; Sanz, M. L.; Ramos, L. J. Chromatogr. A 2017, 1559, 156–163. Wilson, W. B.; Sander, L. C.; Ona-Ruales, J. O.; Mossner, S. G.; Sidisky, L. M.; Lee, M. L.; Wise, S. A. J. Chromatogr. A 2017, 1485, 120–130.
74 ACS Paragon Plus Environment
Page 74 of 99
Page 75 of 99 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
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1792 1793
(170)
1794 1795
(171)
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1799 1800 1801
(175)
Wilson, W. B.; Sander, L. C.; Ona-Ruales, J. O.; Mossner, S. G.; Sidisky, L. M.; Lee, M. L.; Wise, S. A. J. Chromatogr. A 2017, 1484, 73–84. Flieger, J.; Feder-Kubis, J.; Tatarczak-Michalewska, M.; Płazińska, A.; Madejska, A.; Swatko-Ossor, M. J. Sep. Sci. 2017, 40, 2374–2381. Ding, G.; Zhang, W.; Zhang, Z.; Guo, D.; Tang, G.; Li, Y.; Li, J.; Cao, Y. Anal. Bioanal. Chem. 2017, 409, 4581–4592. Tan, T.; Zhang, M.; Wan, Y.; Qiu, H. Talanta 2016, 149, 85–90. Castro Grijalba, A.; Quintas, P. Y.; Fiorentini, E. F.; Wuilloud, R. G. J. Anal. At. Spectrom. 2018, 33, 822–834. Mieszkowski, D.; Sroka, W. D.; Marszałł, M. P. JPC - J. Planar Chromatogr. Mod. TLC 2018, 31, 116–121. Qiao, L.; Lv, W.; Chang, M.; Shi, X.; Xu, G. J. Chromatogr. A 2018, 1559, 141– 148. Li, L.; Zhang, M.; Wang, Y.; Zhou, W.; Zhou, Z. J. Sep. Sci. 2016, 39, 4136–4146. Wang, Q.; Xu, L.; Xue, Y.-W. J. Liq. Chromatogr. Relat. Technol. 2016, 39, 598– 606. Wu, Q.; Sun, Y.; Gao, J.; Chen, L.; Dong, S.; Luo, G.; Li, H.; Wang, L.; Zhao, L. New J. Chem. 2018, 42, 8672–8680. Han, M.; Li, W.; Chen, R.; Han, Y.; Liu, X.; Wang, T.; Guo, H.; Qiao, X. J. Chromatogr. A 2018, 1572, 82–89. Caban, M.; Stepnowski, P. Anal. Chim. Acta 2017, 967, 102–110. Liu, Y.; Yu, H. J. Sep. Sci. 2017, 40, 1660–1666. (Petruczynik, A.; Misiurek, J.; Serafin, S.; Waksmundzka-Hajnos, M. J. Liq. Chromatogr. Relat. Technol. 2017, 40, 252–258. He, S.; He, Y.; Cheng, L.; Wu, Y.; Ke, Y. Chirality 2018, 30, 670–679. Zhang, H.; Bai, L.; Wei, Z.; Liu, S.; Liu, H.; Yan, H. Talanta 2016, 149, 62–68. Wang, S.; Han, C.; Wang, S.; Bai, L.; Li, S.; Luo, J.; Kong, L. J. Chromatogr. A 2016, 1471, 155–163. Fan, C.; Cao, X.; Liu, M.; Wang, W. J. Chromatogr. A 2016, 1436, 133–140. Müller, M.; Englert, M.; Earle, M. J.; Vetter, W. J. Chromatogr. A 2017, 1488, 68– 76. Holzgrabe, U.; Wahl, J. In Capillary Electrophoresis: Methods and Protocols, Schmitt-Kopplin, P., Ed.; Springer New York: New York, NY, 2016, pp 131–153. Kolobova, E.; Kartsova, L.; Kravchenko, A.; Bessonova, E. Talanta 2018, 188, 183–191. Memon, A. F.; Solangi, A. R.; Memon, S. Q.; Mallah, A.; Memon, N. Electrophoresis 2018, 39, 1606–1612. Zhang, Q. Trac-Trends Anal. Chem. 2018, 100, 145–154. Greño, M.; Marina, M. L.; Castro-Puyana, M. J. Chromatogr. A 2018, 1568, 222– 228. Wahl, J.; Holzgrabe, U. J. Pharm. Biomed. Anal. 2018, 148, 245–250. 75 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
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(177) (178)
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(179)
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(180)
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(181) (182)
1812 1813 1814 1815
(183)
1816
(184) (185) (186)
1817 1818 1819 1820 1821 1822
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(188)
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(189)
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(190)
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(191)
1831 1832
(192)
1833 1834
(193)
1835 1836
(194)
1837
(195) (196)
1838 1839 1840 1841 1842 1843
(197) (198) (199)
Wang, Z.; Guo, H.; Chen, M.; Zhang, G.; Chang, R.; Chen, A. Electrophoresis 2018, 39, 2195–2201. Yang, X.; Du, Y.; Feng, Z.; Liu, Z.; Li, J. J. Chromatogr. A 2018, 1559, 170–177. Li, J.; Yu, T.; Xu, G.; Du, Y.; Liu, Z.; Feng, Z.; Yang, X.; Xi, Y.; Liu, J. J. Chromatogr. A 2018, 1559, 178–185. Ling, L.; Xiao, C.; Jiang, L.; Wang, S.; Li, Y.; Chen, X.; Guo, X. New J. Chem. 2017, 41, 12241–12249. Guo, M.; Zhai, Y.; Guo, C.; Liu, Y.; Tang, D.; Pan, Y. Anal. Chim. Acta 2015, 865, 31–38. Zhao, X.; Shen, S.; Wu, D.; Cai, P.; Pan, Y. Anal. Chim. Acta 2017, 985, 114–120. Leipert, J.; Bobis, I.; Schubert, S.; Fickenscher, H.; Leippe, M.; Tholey, A. Anal. Bioanal. Chem. 2018, 410, 4737–4748. Do, T. D.; Comi, T. J.; Dunham, S. J. B.; Rubakhin, S. S.; Sweedler, J. V. Anal. Chem. 2017, 89, 3078–3086. Abdelhamid, H. N.; Khan, M. S.; Wu, H. Anal. Chim. Acta 2014, 823, 51–60. Shrivas, K.; Tapadia, K. J. Chromatogr. B 2015, 1001, 124–130. Kosyakov, D. S.; Anikeenko, E. A.; Ul, N. V; Khoroshev, O. Y.; Shavrina, I. S.; Gorbova, N. S. Anal. Bioanal. Chem. 2018, in press, DOI: 10.1007/s00216-0181353-7. Gabriel, S. J.; Pfeifer, D.; Schwarzinger, C.; Panne, U.; Weidner, S. M. Rapid Commun. Mass Spectrom. 2014, 28, 489–498. Yoon, D.; Lee, D.; Lee, J. H.; Cha, S.; Oh, H. Bin. Rapid Commun. Mass Spectrom. 2015, 29, 213–219. Liu, H.; Dai, J.; Zhou, J.; Huang, H.; Chen, F.; Liu, Z. Int. J. Mass Spectrom. 2015, 376, 85–89. Kucherov, F. A.; Egorova, K. S.; Posvyatenko, A. V; Eremin, D. B.; Ananikov, V. P. Anal. Chem. 2017, 89, 13374–13381. Breitbach, Z. S.; Berthod, A.; Huang, K.; Armstrong, D. W. Mass Spectr. Rev. 2016, 35, 201–218. Dodbiba, E.; Xu, C.; Payagala, T.; Wanigasekara, E.; Moon, H.M.; Armstrong, D. W. Analyst 2011, 1586–1593. Xu, C.; Guo, H.; Breitbach, Z. S.; Armstrong, D. W. Anal. Chem. 2014, 86, 2665– 2672. Lee, J.; Kim, S.; Lee, S.; Rhee, J.; Young, S.; Na, Y. Anal. Chim. Acta 2017, 984, 223–231. Xu, C.; Costa Pinto, E.; Armstrong, D. W. Analyst 2014, 139, 4169–4175. Guo, H.; Dolzan, M. D.; Spudeit, D. A.; Xu, C.; Breitbach, Z. S.; Sreenivasan, U.; Armstrong, D. W. Int. J. Mass Spectrom. 2015, 389, 14–25. Rao, W.; Pan, N.; Tian, X.; Yang, Z. J. Am. Soc. Mass Spetrom. 2016, 27, 124–134. Pan, N.; Rao, W.; Standke, S. J.; Yang, Z. Anal. Chem. 2016, 88, 6812–6819. Wang, Y.; Du, S.; Armstrong, D. W.; Armstrong, D. W. Anal. Bioanal. Chem. 2018, 410, 4725–4735. 76 ACS Paragon Plus Environment
Page 76 of 99
Page 77 of 99 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
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(210)
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(214)
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(219)
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(221)
1882 1883
(222)
1884 1885
(223)
Santos, I. C.; Guo, H.; Mesquita, R. B. R.; Rangel, A. O. S. S.; Armstrong, D. W.; Schug, K. A. Talanta 2015, 143, 320–327. Guo, H.; Breitbach, Z. S.; Armstrong, D. W. Anal. Chim. Acta 2016, 912, 74–84. Guo, H.; Riter, L. S.; Wujcik, C. E.; Armstrong, D. W. Talanta 2016, 149, 103–109. Abu-Lebdeh, Y.; Hammami, A.; Abouimrane, A.; Armand, M. Electrochem. commun. 2017, 81, 112–115. Baldo, M. A.; Oliveri, P.; Simonetti, R.; Daniele, S. Talanta 2016, 161, 881–887. Rizzo, S.; Arnaboldi, S.; Cirilli, R.; Gennaro, A.; Isse, A. A.; Sannicolò, F.; Mussini, P. R. Electrochem. commun. 2018, 89, 57–61. Mousavi, M. P. S.; Wilson, B. E.; Kashefolgheta, S.; Anderson, E. L.; He, S.; Bühlmann, P.; Stein, A. ACS Appl. Mater. Interfaces 2016, 8, 3396–3406. Joshi, V. S.; Kreth, J.; Koley, D. Anal. Chem. 2017, 89, 7709−7718. Karimi-Maleh, H.; Shojaei, A. F.; Tabatabaeian, K.; Karimi, F.; Shakeri, S.; Moradi, R. Biosens. Bioelectron. 2016, 86, 879–884. Gomes, R. N.; Sousa, C. P.; Casciano, P. N. S.; Ribeiro, F. W. P.; Morais, S.; de Lima-Neto, P.; Correia, A. N. Mater. Sci. Eng. C 2018, 88, 148–156. Wu, F.; Huang, T.; Hu, Y.; Yang, X.; Ouyang, Y.; Xie, Q. Microchim. Acta 2016, 183, 2539–2546. Roushani, M.; Valipour, A. Sensors Actuators B Chem. 2016, 222, 1103–1111. Sanati, A. L.; Faridbod, F.; Ganjali, M. R. J. Mol. Liq. 2017, 241, 316–320. Ueda, H.; Yoshimura, T.; Nishiyama, K.; Yoshimoto, S. Langmuir 2017, 33, 13468–13479. Abo-Hamad, A.; AlSaadi, M. A.; Hayyan, M.; Juneidi, I.; Hashim, M. A. Electrochim. Acta 2016, 193, 321–343. Polo-Luque, M. L.; Simonet, B. M.; Valcárcel, M. TrAC Trends Anal. Chem. 2013, 47, 99–110. Chaiyo, S.; Mehmeti, E.; Zagar, K.; Siangproh, W.; Kalcher, K. Anal. Chim. Acta 2016, 918, 26–34. Beitollahi, H.; Ivari, S. G.; Torkzadeh-Mahani, M. Biosens. Bioelectron. 2018, 110, 97–102. Arabali, V.; Ebrahimi, M.; Abbasghorbani, M.; Gupta, V. K.; Farsi, M.; Ganjali, M. R.; Karimi, F. J. Mol. Liq. 2016, 213, 312–316. Bavandpour, R.; Karimi-Maleh, H.; Asif, M.; Gupta, V. K.; Atar, N.; Abbasghorbani, M. J. Mol. Liq. 2016, 213, 369–373. Alavi-Tabari, S. A. R.; Khalilzadeh, M. A.; Karimi-Maleh, H. SJ. Electroanal. Chem. 2018, 811, 84–88. Karimi-Maleh, H.; Rostami, S.; Gupta, V. K.; Fouladgar, M. J. Mol. Liq. 2015, 201, 102–107. Li, J.; Wang, Y.; Sun, Y.; Ding, C.; Lin, Y.; Sun, W.; Luo, C. RSC Adv. 2017, 7, 2315–2322. Cheraghi, S.; Taher, M. A.; Karimi-Maleh, H. J. Food Compos. Anal. 2017, 62, 254–259. 77 ACS Paragon Plus Environment
Analytical Chemistry 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1886 1887 1888 1889 1890 1891 1892 1893 1894
(224) (225) (226) (227) (228) (229) (230)
1895 1896
(231)
1897
(232) (233)
1898 1899 1900 1901
(234)
1902
(235) (236)
1903 1904 1905 1906
(237)
1907 1908
(238)
1909 1910
(239)
1911
(240) (241)
1912 1913
Govindhan, M.; Chen, A. Microchim. Acta 2016, 183, 2879–2887. Damiri, S.; Oskoei, Y. M.; Fouladgar, M. J. Exp. Nanosci. 2016, 11, 1384–1401. Atta, N. F.; Galal, A.; Ahmed, Y. M. J. Electrochem. Soc. 2018, 165, B442–B451. Hosseini, F. Int. J. Electrochem. Sci. 2018, 4923–4932. Atta, N. F.; El-Ads, E. H.; Ahmed, Y. M.; Galal, A. Electrochim. Acta 2016, 199, 319–331. El-Hady, D. A.; Albishri, H. M. Talanta 2015, 139, 150–158. Arkan, E.; Saber, R.; Karimi, Z.; Shamsipur, M. Anal. Chim. Acta 2015, 874, 66– 74. Nagles, E.; García-Beltrán, O.; Calderón, J. A. Electrochim. Acta 2017, 258, 512– 523. Valipour, A.; Roushani, M. Microchim. Acta 2017, 184, 2015–2022. Rzhevskaia, A. V.; Shvedene, N. V.; Pletnev, I. V. J. Electroanal. Chem. 2016, 783, 274–279. Mazloum-Ardakani, M.; Hosseinzadeh, L.; Khoshroo, A. J. Electroanal. Chem. 2015, 757, 58–64. Fei, J.; Dou, W.; Zhao, G. Microchim. Acta 2015, 182, 2267–2275. Wang, X.; Wang, Y.; Ye, X.; Wu, T.; Deng, H.; Wu, P.; Li, C. Biosens. Bioelectron. 2018, 99, 34–39. Li, T.; Yao, T.; Zhang, C.; Liu, G.; She, Y.; Jin, M.; Jin, F.; Wang, S.; Shao, H.; Wang, J. RSC Adv. 2016, 6, 66949–66956. Wang, Y.; Han, M.; Liu, G.; Hou, X.; Huang, Y.; Wu, K.; Li, C. Biosens. Bioelectron. 2015, 74, 792–798. Sun, Y.; Zheng, H.; Wang, C.; Yang, M.; Zhou, A.; Duan, H. Nanoscale 2016, 8, 1523–1534. Chen, S.; Wei, L.; Chen, X.; Wang, J. Anal. Chem. 2015, 87, 10902−10909. Wang, C.; Ye, X.; Wang, Z.; Wu, T.; Wang, Y.; Li, C. Anal. Chem. 2017, 89, 12391– 12398.
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Figure Captions
1917
Figure 1.
1918
derivatives.
1919
Figure 2.
1920
after PIL-SPME for the determination of acrylamide in (A) in-solution brewed coffee spiked
1921
with 100 g·L-1, and (B) brewed coffee un-spiked (pink) and spiked with 50 g·L-1 (blue)
1922
and 100 g·L-1 (black). Reprinted from J. Chromatogr. A, Vol. 1459, Cagliero, C.; Nan, H.;
1923
Bicchi, C.; Anderson, J. L. Matrix-compatible sorbent coatings based on structurally-tuned
1924
polymeric ionic liquids for the determination of acrylamide in brewed coffee and coffee
1925
powder using solid-phase microextraction, pp. 17–23 (ref 41). Copyright 2018, with
1926
permission from Elsevier.
1927
Figure 3.
1928
using the IL-ABS based on tetrabutyltetradecylphosphonium chloride ([P4.4.4.14+][Cl-]) and
1929
HCl. Reproduced from Ionic-liquid-based acidic aqueous biphasic systems for simultaneous
1930
leaching and extraction of metallic ions, Gras, M.; Papaiconomou, N.; Schaeffer, N.; Chainet,
1931
E.; Tedjar, F.; Coutinho, J. A. P.; Billard, I. Angew. Chem. - Int. Ed., Vol. 57, Issue 6 (ref
1932
94), Copyright 2018 Wiley.
1933
Figure 4.
1934
based GC stationary phases of the Watercol series. The CLP oil was analyzed using the
1935
following IL-based GC stationary phases: Watercol 1460 at 70 ºC (A), Watercol 1900 at 70
1936
ºC (B), and Watercol 1910 at 150 ºC (C). The transformer oil (RM 8506a) was analyzed
1937
using the followed IL-based GC stationary phases: Watercol 1460 at 50 ºC (D), Watercol
1938
1900 at 50 ºC (E), and Watercol 1910 at 50 ºC (F). Reproduced from Frink, L. A.; Armstrong,
Chemical structures of the major cations and anions that compose ILs and IL
GC-MS chromatogram in the selected ion monitoring (SIM) mode obtained
Influence of the extraction temperature in the separation of Co2+ and Ni2+ ions
Representative chromatograms of the determination of water in oil using IL-
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1939
D. W. Anal. Chem. 2016, 88, 8194–8201 (ref 137). Copyright 2016 American Chemical
1940
Society.
1941
Figure 5.
1942
obtained using the SLB-IL111i stationary phase in the first dimension combined with
1943
different IL-based stationary phases in the second dimension: (a) SLB-IL76, (b) SLB-IL60,
1944
and (c) SLB-IL59. The conventional SLB-IL111/SLB-IL59 column set was included for
1945
comparison in (d). Reprinted by permission from Springer Nature GmbH: Springer Nature,
1946
Anal. Bioanal. Chem., Ionic liquid phases with comprehensive two-dimensional gas
1947
chromatography of fatty acid methyl esters, Pojjanapornpun, S.; Nolvachai, Y.; Aryusuk, K.;
1948
Kulsing, C.; Krisnangkura, K.; Marriott, P. J. (ref 143). Copyright 2018 Springer.
1949
Figure 6.
1950
a traditional matrix based on 2,5-dihydroxybenzoate (DHB, on the top), and IL-based
1951
matrixes (2,5-dihydroxybenzoate/N-methylaniline, DHB/N-MA, at the middle, and 2,5-
1952
dihydroxybenzoate/N-ethylaniline, DHB/N-EA, at the bottom). The mass spectra were
1953
acquired in reflectron mode. The analyzed sample was 0.5 mL of solution (before drying)
1954
containing 10 pmol of the analyte. The degrees of polymerization were annotated with red
1955
dashed line. Reprinted from Anal. Chim. Acta, Vol. 985, Zhao, X.; Shen, S.; Wu, D.; Cai, P.;
1956
Pan, Y. Novel ionic liquid matrices for qualitative and quantitative detection of carbohydrates
1957
by matrix assisted laser desorption/ionization mass spectrometry, pp. 114–120 (ref 181).
1958
Copyright 2017, with permission from Elsevier.
1959
Figure 7.
1960
metabolites (phosphoethanolamines, PEs, and phosphatidylglycerols, PGs) in single cells.
1961
(a) Mass spectra obtained after ESI-MS: the [PG (34:1) + Na]+ (771.5152 m/z) is
Representative contour plots of the separation of a 37 FAME mix in GC × GC
MALDI-TOF spectra of the polysaccharides D2000 (A) and D4000 (B) using
Comparison between ESI-MS and PIESI-MS for the determination of
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Analytical Chemistry
1962
indistinguishable from a 13C isotopic peak of [PE(P-38:6) + Na]+ (771.5125 m/z). (b) Mass
1963
spectra obtained after PIESI-MS, showing the [PG (34:1) − H +[C5(C4Pyr)22+]]+ (1071.8672
1964
m/z) peak. (c) Mass spectra obtained after PIESI-MS, showing the [PG (34:1) − H +
1965
[C3(P3,3,3)22+]]+ (1109.8389 m/z) peak. PE(P-38:6) was detected [C43H74NO7P+Na]+
1966
(771.5125 m/z) in (b) and (c) using the dicationic compounds (not shown). [C5(C4Pyr)22+] is
1967
the 1,5-pentanediyl-bis(1-butylpyrrolidinium) cation, and [C3(P3,3,3)22+] is the P,P’-propyl-
1968
bis(tripropylphosphonium) cation. Reproduced from Pan, N.; Rao, W.; Standke, S. J.; Yang,
1969
Z. Anal. Chem. 2016, 88, 6812–6819 (ref 198). Copyright 2016 American Chemical Society.
1970
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Table 1.
Page 82 of 99
Representative microextraction procedures based on the use of magnetic ionic liquids (MILs).
Analytes
Sample
Extraction procedurea Dispersive liquid-liquid microextraction PAHs Water and DLLME tea infusion Pharmaceutical drugs, phenolics, insecticides, and PAHs UV filters
Water
DLLME
Water
SBDLME
Sequence specific DNA
Cell lysate
DLLME
Sequence specific DNA
Cell lysate
DLLME
-
DLLME
Escherichia Coli K12 Estrogens
Urine
DLLME
Organic pollutants
Water
DLLME
DNA
Plasma
DLLME
Extraction materialb
Analytical techniquec
LODd (µg·L1)
RSDe (%)
Ref.
[N8,8,8,B+][FeBrCl3-]g, [N8,8,8,MOB+][FeBrCl3-], or [(BBnIM)2C122+][NTf2,FeCl3Br-] [P6,6,6,14+]2[MnCl42-]g, [N1,8,8,8+]2[MnCl42-] or [Aliquat+]2[MnCl42-] [P6,6,6,14+][Dy(hfacac)4-], [P6,6,6,14+][Co(hfacac)3-], or [P6,6,6,14+][Ni(hfacac)3]g + [P6,6,6,14 ][Mn(hfacac)3-]
HPLC-FD
0.005–0.02
1.0–13
(72)
HPLC-UV
0.25–1.00
6.1-19.6
(73)
TD-GC-MS
0.01–0.03
1.4–15
(74)
HPLC-UV and qPCR HPLC-UV and qPCR
-
-
(75)
-
-
(76)
Cell culture and qPCR
100 CFU mL-
7–12.5
(77)
HPLC-UV
2
4.7–19
(78)
HPLC-UV
0.05–1.0
0.3–17
(79)
qPCR
-
8.5–12.8
(80)
[P6,6,6,14+][Co(hfacac)3-]g or [P6,6,6,14+][Ni(hfacac)3] [P6,6,6,14+][Ni(hfacac)3-]g, [P6,6,6,14+][Co(hfacac)3-], [P6,6,6,14+][Dy(hfacac)4-], [P6,6,6,14+]2[MnCl42-] or [Aliquat+]2[MnCl42-] [P6,6,6,14+]2[MnCl42-]g, or [Aliquat+]2[MnCl42-] [P6,6,6,14+][Ni(hfacac)3-]g, [P6,6,6,14+][Co(hfacac)3-],
1
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Analytical Chemistry
[P6,6,6,14+][Dy(hfacac)4-], or [P6,6,6,14+][Mn(hfacac)3-]
Single-drop microextraction DNA Cell lysate
DI-SDME
[P6,6,6,14+][Ni(hfacac)3-], [P6,6,6,14+][Co(hfacac)3-]
LAMP and IMSA
Organic pollutants
Water
HS-SDME
HPLC-UV
Free fatty acids
Milk
Vacuum HS-SDME
Chlorobenzenes DNA
Water Plasma
HS-SDME DI-SDME
[P6,6,6,14+]2[MnCl42-]g, or [Aliquat+]2[MnCl42-] [P6,6,6,14+]2[MnCl42-], [Aliquat+]2[MnCl42-], [P6,6,6,14+][Mn(hfacac)3]g, or [P6,6,6,14+][Dy(hfacac)4-] [C2MIM+]2[Co(NCS)42-] [P6,6,6,14+][Ni(hfacac)3-]g, [P6,6,6,14+][Co(hfacac)3-], [P6,6,6,14+][Dy(hfacac)4-], or [P6,6,6,14+][Mn(hfacac)3-]
203–2030 copies per reaction 0.04–1.0
-
(81)
2.3–15
(79)
HSD-GCMS
14.5–21
2.5–13
(82)
TD-GC-MS qPCR
0.004–0.008 -
3–18 8.5–12.8
(83) (80)
Aqueous biphasic system Chloramphenicol Water ABS [TMG+][TEMPO-SO3-]h HPLC-UV 0.14 2.42–4.45 (84) a Abbreviations: ABS for aqueous biphasic system, DLLME for dispersive liquid-liquid microextraction, HS-SDME for headspace single-drop microextraction, vacuum HS-SDME for headspace single-drop microextaction under reduced pressure conditions, DISDME for direct immersion-drop microextraction, and SBDLME for stir-bar dispersive liquid microextraction. b IL abbreviations: Cations: [Aliquat+] for trioctylmethylammonium, [(BBnIM)2C122+] for 1,12-di(3+ + benzylbenzimidazolium)dodecane, [C2MIM ] for 1-ethyl-3-methylimidazolium, [N1,8,8,8 ] for trioctylmethylammonium, [N8,8,8,B+] for benzyltrioctylammonium, [N8,8,8,MOB+] for methozylbenzyltrioctylammonium, [P6,6,6,14+] for trihexyltetradecylphosphonium, and [TMG+] for 1,1,3,3-tetramethylguanidine Anions: [Co(hfacac)3-] for tris(hexafluoroacetylaceto)cobaltate(II), [Co(NCS)42-] for tetraisothiocyanatocobaltate (II), [Dy(hfacac)4] for tetra(hexafluoroacetylaceto)dysprosate(III), [FeBrCl3-] for bromotrichloroferrate(III), [MnCl42-] for tetrachloromanganate(II),
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[Mn(hfacac)3-] for tris(hexafluoroacetylaceto)manganate(II), [Ni(hfacac)3-] for tris(hexafluoroacetylaceto)nickelate(II), [NTf2-] for bis[(trifluoromethyl)sulfonyl]imide, and [TEMPO-OSO3-] for 2,2,6,6-tetramethylpiperidine. c Abbreviations: FD for fluorescence detection, GC for gas chromatography, HPLC for high-performance liquid chromatography, HSD for headspace desorption, IMSA for isothermal multiple-self-matching-initiated amplification, LAMP for loop-mediated isothermal amplification, MS for mass spectrometry, qPCR for quantitative polymerase chain reaction, TD for thermal desorption, and UV for ultraviolet detection. d Limit of detection. e Relative standard deviation. g Selected as optimum MIL. h Molecularly imprinted polymer based on a MIL monomer.
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Analytical Chemistry
Table 2.
Representative applications involving the use of ILs in either the mobile phase or the stationary phase of LC applications.
Analyte / Mobile phasea Sample ILs as mobile phase additives Mandelic acid, Methanol: [(CH2O+ vanilmandelic acid, and Men)C5IM ][Cl ] aqueous solution phenyllactic acid/ (10:90, v/v) Auxinic herbicides/ Acetonitrile: 5 mmol·L-1 [(MIM)2C82+]2[BF4-] aqueous solution at pH 3 (300:7, v/v) Quaternary alkaloids/ Herbal solutions and tablets Hg2+, methylmercury and ethylmercury/ Sea food, yeast and garlic Metabolites/ Human plasma
Acetonitrile: 1% DESe aqueous solution at pH 3.3 (32:68, v/v) Methanol: [C8MIM+][Cl-] in 0.1 mol·L-1 NaCl and 0.02 mol L-1 citric/citrate buffer, pH 2.0 (99.6:0.4) Acetonitrile: water: [C2MIM+][BF4-] (50:50:1.5, v/v)
ILs as components of the stationary phase Flavonoids, nucleosides Acetonitrile: 10 mmol·L-1 and amino acids/ ammonium formate aqueous solution (90:10, v/v), gradient Soybeans, urine elution
Stationary phasea (dimensions)
Separation modeb
Analytical techniquec
LODd (µg·L-1)
Ref.
Astec Chirobiotic T column (150 mm L × 4.6 mm ID × 5 µm) Kromasil ODS C18 column (250 mm L × 4.6 mm ID × 5 µm) ODS C18 column (150 mm L × 4.6 mm ID × 5 µm) Hypersil GOLD aQ C18 column (150 mm L × 4.6 mm ID)
Chiral
HPLC-DAD
-
(152)
RP
HPLC-UV
-
(153)
RP
HPLC-UV
6–20
(154)
RP
HPLC-CVAFS
0.05–0.11 (155)
Silica gel F254 60RP-18 glass plate (20 cm × 10 cm)
RP
HPTLC-De
0.18–0.39 (156) µg·spot-1
SCIL amidefunctionalized based on [V(AcNH2)IM+][Br] column (150 mm L × 3 mm ID × 5 µm)
IEC / HILIC
HPLC-MS
-
(157)
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-nitroethanol, aromatic alcohols, mandelic acid derivatives, amino acids, ferrocenes, and drugs Non-steroidal antiinflammatory drugs, nucleobases- nucleotides mixtures, and alkaloidsglycosides mixtures/ Cortex phellodendri extract
Anilines, phenols, and PAHsg/ -
Alkaloids, glycosides, aromatic acids and amino acids -
Chiral -CDf silica confined modified with pyridinium column based ILs (250 mm L × 4.6 mm ID × 5 µm) Acetonitrile: ammonium formate SCIL γaqueous solution (50:50, v/v), glycidoxypropylgradient elution functionalized zwitterionic IL with quaternary ammonium and sulfonate groups column (150 mm L × 2.1 mm ID × 5 µm) Methanol: water (different Graphene quantum compositions depending on the dot silica confined group of analytes) column modified with [(C2NH2)MIM+][Br] (250 mm L × 4.6 mm ID × 5 µm) Acetonitrile: ammonium acetate Graphene quantum (different compositions depending dot silica confined on the group of analytes) column modified with [(C2NH2)MIM+][Br] Methanol: water (50:50, v/v)
Page 86 of 99
RP
HPLC-UV
-
(158)
RP and HILIC
HPLC-UV
-
(159)
RP
HPLC-UV
-
(160)
HILIC
HPLC-UV
-
(160)
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Analytical Chemistry
(250 mm L × 4.6 mm ID × 5 µm) (250 mm L × 4.6 mm ID × 5 µm) Alkylbenzenes and Acetonitrile:water (70:30, v/v) POSMh hybrid RP Nano-LC(161) amides monolith modified UV with L-Cys and [VC4IM+][Br-] (100 µm ID) Glycoproteinnon0.1% trifluoroacetic acid in POSMh hybrid Mixed Nano-LC(161) glycoprotein mixtures, acetonitrile: 0.1% trifluoroacetic monolith modified mode UV and TARG1 protein/ acid in water, gradient elution with L-Cys and [VC4IM+][Br-] (100 µm ID) a IL abbreviations: Cations: [(CH O-Men)C IM+] for 1-[(1R,2S,5R)-(−)-menthoxymethyl]-3-pentylimidazolium, [C MIM+] for 22 5 2 ethyl-3-methylimidazolium, [(C2NH2)MIM+] for 1-aminoethyl-3-methylimidazolium, [C8MIM+] for 1-octyl-3-methylimidazolium, [(MIM)2C82+] for 1,12-di(3-methylmidazolium)octane, [V(AcNH2)IM+] for 1-vinyl-3-acetamideimidazolium, and [VC4IM+] for 1vinyl-3-butylimidazolum. Anions: [BF4-] for tetrafluoroborate, [Br-] for bromide, and [Cl-] for chloride. b Abbreviations: Chiral: chiral separation, HILIC: hydrophilic interaction liquid chromatography, and RP: reversed-phase. c Abbreviations: CV-AFS: cold vapor atomic fluorescence spectrometry, DAD: diode array detection, De: densitometry, HPLC: highperformance liquid chromatography, HPTLC: high performance thin layer chromatography, MS: mass spectrometry, Nano-LC: nano-liquid chromatography, and UV: ultraviolet detection. c Limit of detection. e Choline chloride as hydrogen bond acceptor and ethylene glycol as hydrogen bond donor, mixed in a 1:3 molar ratio. f -Cyclodextrin. g Polycyclic aromatic hydrocarbons. h Polyhedral oligomeric silesquioxane methacrylate.
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Table 3.
Page 88 of 99
Representative IL-modified electrochemical biosensors to determine different compounds in biological samples.
Analyte Glassy Carbon Electrodes Ascorbic acid, dopamine and uric acid Glycoprotein hormone Nitric oxide Anti-hepatitis C drugs Neurotransmitters Vitamins B2, B6 and C Carbon Paste Electrodes 6-Mercaptopruine, 6thioguanine and dasatinib (anticancer drugs) Levedopa Thyroid stimulating hormone Adrenaline Doxorubicin and dasatinib Tramadol HER2 (enzyme)
Sample
ILa
LODb (µg·L-1)
Ref.
Urine
[C3MIM+][Cl-]
1760, 765, and 5 3.5·10-4 c 3.9
(210)
Serum Serum and urine Blood serum Urine Plasma
[C8MIM+][BF4-] [C4MIM+][Cl-] [C4MPip+][PF6-]
0.24
(226)
0.002 500–1000
(228) (229)
Urine
[C4MIM+][PF6-]
IL/Pt/carbon nanotubes
1.4, 8.4, and 488
(208)
Serum and urine Serum Urine Serum
[C4MIM+][PF6-]
IL/graphene quantum dots
2.7
(212)
[C4Py+][PF6-] [C3C3IM+][Br-] [C4MIM+][BF4-]
IL/nanogold/antibody IL/CuFe2O4 nanoparticles IL/ZnO nanoparticles
(217) (219) (220)
[C3C3IM+][Br-] [C2MIM+][PF6-]
IL/MgO/carbon nanotubes IL/Au nanoparticles / nanotubes
0.10 13 4887 and 244 2.1 10
Urine Serum
[C4MPip+][PF6-] [C8MIM+][PF6-]
Biosensor Graphene/IL Graphene/chitosan/IL IL/Pt and W nanoparticles anchored to reduced graphene oxide IL/multi-walled carbon nanotubes/cobalt nanoparticles IL/cyclodextrin IL/human serum albumin, and IL/bovine serum albumin
carbon
(211) (224)
(227) (230)
Screen Printed Electrodes
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Analytical Chemistry
Diclofenac
Urine
[C4MIM+][Cl-]
Uric acid and dopamine Hepatitis C virus
Urine Serum
[C4MIM+][BF4-] [C8MIM+][BF4-]
Thiocyanate
Saliva
[C10C10IM+][Br-]
Isoprenaline and aspirin
Urine
[C6MIM+][PF6-]
Factor α antigen (biomarker tumor necrosis)
Serum
[C4MIM+][NTf2-]
Salmonella pullorum and Salmonella gallinarum
Eggs and chicken meat
Molecularly Imprinted Materials Neuronspecific enolase Serum
Ractopamine
Urine
[C4MIM+][PF6-]
[(C3SH)VIM+][ BF4-] as MIL template and [(PyrC3)2IM+][Br-] as crosslinker [C4Py+][PF6-]
IL/cobalt hexacyanoferrate nanoparticles modified multi-walled carbon nanotubes IL/carbon nanotubes IL/nafion/TiO2
Screen-printed electrodes with IL solid-state ZnO/IL IL/fullerene-functionalized multiwalled carbon nanotubes/antibody IL/Au nanoparticles /antibody
MIP-PIL/PIL/GCE
89
(225)
24 and 29 2.5·10-5
(231) (232)
174
(233)
63.3 and 126
(221)
5·10-3
(234)
1x104 cfu · mL−1
(235)
2.6·10-3
(236)
MIP-PIL/gold 126 (237) nanoparticles/graphene Bovine serum albumin Milk [(NH2C3)VIM+][PF6-] MIP-PIL/ carboxyl functionalized 99 (238) multi-walled carbon nanotubes a IL abbreviations: Cations: [C C IM+] for 1,3-dipropylimidazolium, [C C IM+] for 1,3-didecylimidazolium, [C MIM+] for 1-ethyl3 3 10 10 2 3-methylimidazolium, [C3MIM+] for 1-propyl-3-methylimidazolium, [(C3SH)VIM+] for 1-(3-mercaptopropyl)-3-vinylimidazolium, [C4MIM+] for 1-butyl-3-methylimidazolium, [C6MIM+] for 1-hexyl-3-methylimidazolium, [C4MPip+] for 1-butyl-1methylpiperidinium, [C4Py+] for 1-butylpyridinium, [C8MIM+] for 1-octyl-3-methylimidazolium, [(NH2C3)VIM+] for 3-(3aminopropyl)-1-vinylimidazolium, and [(PyrC3)2IM+] for 1,3-di(3-N-pyrrolpropyl)imidazolium. 89 ACS Paragon Plus Environment
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Page 90 of 99
Anions: [BF4-] for tetrafluoroborate, [Br-] for bromide, [Cl-] for chloride, [NTf2-] for bis[(trifluoromethyl)sulfonyl]imide, and [PF6] for hexafluorophosphate. b Limit of detection. C Milli-international units per milliliter.
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Analytical Chemistry
(A) Cations
(B) Anions
Imidazolium
Pyrrolidinium
Pyridinium
+
+
+
Bis[(trifluoromethyl)sulfonyl]amine
Alkylsulphonate
–
Triflate
–
Chloride
–
Cl
–
Bromide [R1R2IM+] Benzimidazolium
+
[NTf2
[R1R2Pyr+]
[R1Py+]
Ammonium
Phosphonium
+
–]
[RSO3
Tetrafluoroborate
+
–]
[CF3SO3
Hexafluorophosphate
–
–
–]
or
[TfO –]
[R1R2BIM ]
+
[NR1,R2,R3,R4 ]
F C2F5
P
–
[PR1,R2,R3,R4 ]
+
Guanidinium
+
Paramagnetic anions Tetrachloroferrate(III)
Tetrachloromanganate(II)
Cl
Cl [R1R2Pip+]
[(R1R2)(R3R4)(R5R6)Gu+]
F [FAP –]
[PF6–]
Choline
+
C2F5
C 2F 5
+
[BF4–] Piperidinium
–
Tris(pentafluoroethyl)trifluorophosphate
F +
Br
[Ch+]
Fe Cl
– Cl Cl
[FeCl4–]
Mn Cl
Tris(hexafluoroacetylaceto)manganate(II)
–
2– Cl Cl
[MnCl42–]
[Mn(hfacac)3 –]
Figure 1
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Figure 2
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Figure 3
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Figure 4
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Figure 5
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Figure 6
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Figure 7
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299x168mm (200 x 200 DPI)
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