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Compact Ultra-high Pressure Nano-flow Capillary Liquid Chromatograph Xiaofeng Zhao, Xiaofeng Xie, Sonika Sharma, Luke T Tolley, Alex Plistil, Hal E. Barnett, Martin Brisbin, Adam C. Swensen, John Calvin Price, Paul B Farnsworth, H. Dennis Tolley, Stanley D. Stearns, and Milton L. Lee Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/acs.analchem.6b03575 • Publication Date (Web): 29 Nov 2016 Downloaded from http://pubs.acs.org on November 30, 2016
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Analytical Chemistry
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Compact Ultra-high Pressure Nano-flow Capillary Liquid Chromatograph
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Xiaofeng Zhao,†a Xiaofeng Xie,†a Sonika Sharma,† Luke T. Tolley,‡ Alex Plistil,§ Hal E.
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Barnett,§ Martin P. Brisbin,§ Adam C. Swensen,† John C. Price,† Paul B. Farnsworth,† H. Dennis
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Tolley,|| Stanley D. Stearns,§ and Milton L. Lee*, †
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†Department of Chemistry and Biochemistry, Brigham Young University, Provo, UT 84602, USA
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‡
Department of Chemistry and Biochemistry, Southern Illinois University, Carbondale, IL 62901, USA
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§
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||
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†a
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*
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ABSTRACT: A compact ultra-high pressure nano-flow liquid chromatograph (LC) was
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developed with the purpose in mind of creating a portable system that could be easily moved to
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various testing locations or placed in close proximity to other instruments for optimal coupling,
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such as with mass spectrometry (MS). The system utilized innovative nano-flow pumps,
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integrated with very low volume stop-flow injector and mixing tee. The system weighed only 5.9
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kg (13 lbs), or 4.5 kg (10 lbs) without controller, and could hold up to 1100 bar (16,000 psi)
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pressure. The total volume pump capacity was 60 µL. In this study, the sample injection volume
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was determined by either a 60 nL internal sample groove machined in a high pressure valve rotor
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or by a 1 µL external sample loop, although other sample grooves or loops could be selected.
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The gradient dwell volume was approximately 640 nL, which allowed significant reduction in
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sample analysis time. Gradient performance was evaluated by determining the gradient step
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accuracy. A low RSD (0.6%, n = 4) was obtained for day-to-day experiments. Linear gradient
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reproducibility was evaluated by separating a three-component polycyclic aromatic hydrocarbon
VICI, Valco Instruments, Houston, Texas 77055, USA
Department of Statistics, Brigham Young University, Provo, UT 84602, USA These two authors contributed equally to this work.
Corresponding author:
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mixture on a commercial 150 µm inner diameter capillary column packed with 1.7 µm particles.
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Good retention time reproducibility (RSD < 0.17%) demonstrated that the pumping system could
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successfully generate ultra-high pressures for use in capillary LC. The system was successfully
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coupled to an LTQ Orbitrap MS in a simple and efficient way; LC-MS of a trypsin-digested
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bovine serum albumin (BSA) sample provided narrow peaks, short dwell time and good peptide
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coverage.
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Introduction Ultra-high pressure liquid chromatography (UHPLC) has been around for almost two
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decades, introduced to overcome the pressure limitations of conventional pumping systems and
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to allow the use of very small particles as stationary phases.1-3 Due to its excellent separation
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efficiency, short analysis time, low solvent consumption and easy coupling to mass spectrometry
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(MS), UHPLC has become a very popular and green analytical tool, and is becoming widely
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used for environmental, biochemical and pharmaceutical analysis.4-10 Very small particles (sub-2
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µm) can result in improved performance in LC, as well as high speed separations.1,11-14 However,
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without shortening the column length, the use of small particles requires high pressures. While
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typically not an issue with small diameter capillary columns, operating at high pressures can
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create frictional heating, which can impact the retention of solutes and, in some cases, cause
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decomposition1,14 and loss in column efficiency.15,16 Heat dissipation can be facilitated by
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reducing the column diameter.1,12,17 Small diameter packed fused silica columns allow fast heat
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dissipation, low organic solvent usage and minimal waste generation.
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The first UHPLC system for capillary columns packed with 1.5 µm nonporous silica particles was a home-built system reported by Jorgenson’s group.1 The same group also
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constructed a gradient UHPLC system and separated a tryptic protein digest using 1.0 µm
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particles at 9000 bar.2 However, the system was very large, inconvenient, and not amenable to
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routine use. A subsequent UHPLC system was constructed by modifying a Waters Model 6000
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pump, which was coupled to a tandem MS using a capillary packed with 1.5 µm nonporous
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particles.18 This system demonstrated a high duty cycle, good signal-to-noise and full automation.
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This work led to the introduction of commercial UHPLC instrumentation in 2004.19 Currently,
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more than 20 different UHPLC systems are commercially available, with upper pressure limits
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between 600-1500 bar.4,20,21 An excellent review by Eeltink et al.22 of advancements in UHPLC
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instrumentation and practice were recently published. This review includes improvements in
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column technology, pump design, sample introduction, temperature effects, and methods
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development. UHPLC systems with pressures up to 20,000 psi, submicron porous particles and
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automated switching valves with large external sample loops (5-10 µL) are readily available.
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However, most of these systems are limited to laboratory bench operation, and cannot be easily
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moved from one place to another or used for field applications. Furthermore, when coupled to
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MS or other instruments in the laboratory, long connecting tubing is often needed, which can
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greatly reduce the performance and throughput of the UHPLC system.
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Compared to standard columns, e.g., 4.6-1.0 mm i.d., extra-column band broadening
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becomes much more critical when using smaller internal diameter columns.21 Fekete et al.
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compared the extra-column peak variance contributions of several commercially available LC
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systems, and concluded that losses in efficiency can reach 30–55% with these UHPLC systems,
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even when optimized.23 Further improvements in instrumental design could be achieved by using
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smaller volume capillary fitting, smaller and shorter connecting capillary tubing and a smaller
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volume detector cell to reduce detrimental extra-column dead-volume.21, 23-27 Furthermore, small
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dwell volume is also highly desirable for UHPLC.21
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The injection system for UHPLC should hold extremely high pressure, deliver a
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reproducible small volume, eliminate all carryover and minimize brand spreading.28 Static-split
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injection technology was reported by Jorgenson’s group, which withstood high pressures.1,2,29
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Wu et al. used a pressure-balanced injection method to introduce sample, and found it to be
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effective and reproducible.3 A commercial system (Waters ACQUITY UPLC) uses a flow-
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through-needle injector.30 The gradient passes through the needle during injection, ensuring
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complete sample transfer. In addition to the above-mentioned concerns, the detector data-
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acquisition rate is also very important. Narrow peaks (as small as 1 s in some cases) require at
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least 10-15 data points per peak to accurately specify resolution.21
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Significant effort has been made in the past to miniaturize LC.31-35 However, little effort
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has been made to miniaturize UHPLC. Recently, we reported a compact gradient LC system with
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an LED UV-absorption detector (260 nm).32 This system meets many of the requirements for
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field-portability, i.e., light-weight (9 lbs), low mobile phase consumption and waste generation,
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and battery operation. The pressure generated by this pump reaches up to 8,000 psi. Although
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nano-flow UHPLC systems are commercially available, they are not yet portable. With parallel
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successful efforts in miniaturization of MS, compact UHPLC-MS can be expected in the future,
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which would certainly be attractive for field analysis.36
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An important application for UHPLC is MS-based proteomics.37 Due to the complex
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nature of protein/peptide samples, integrated UHPLC-MS is commonly used to analyze these
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samples. UHPLC is used prior to MS to separate complex mixtures of peptides or proteins for
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accurate identification and quantitation. By using long columns, high pressures, small particles
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and long gradients, peak capacities as large as 1500 have been achieved for UHPLC-MS based
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proteomics.38 Iwasaki et al. identified 41,319 typtic peptides from 5,970 proteins using an 8 h
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gradient and 4 m long monolithic column.39 High separation power, fast analysis, small sample
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volume and easy coupling to MS are some of the key requirements for an UHPLC system used
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for proteomics. As demonstrated in our previous research, one important aspect of miniature LC
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is small dwell volume.32 For LC-MS based proteomics, small dwell volume will lead to less
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extra-column band broadening, higher efficiency, lower carryover, faster analysis (i.e., less time
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for sample to reach the head of the column), and higher sample throughput. In addition, a
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compact LC will facilitate optimum positioning with the MS inlet. A miniature LC also allows
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coupling of multiple LC units with a single MS to further improve sample throughput.40 A
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simplified portable UHPLC system would reduce the footprint of the system, increase the duty
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cycle, simplify maintenance, reduce costs and improve separation power by reducing extra-
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column volume.
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In this work, a small, portable gradient ultra-high pressure nano-flow pumping system
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was developed and evaluated using an on-column LED-based UV-absorption detector reported
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earlier, 41 as well as with an LTQ Orbitrap MS. The system was designed specifically for
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capillary columns. Gradient performance and separation were evaluated using this new
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integrated UHPLC-UV system. Efficient coupling of the nano-flow UHPLC to an Orbitrap MS
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for analyzing trypsin-digested BSA for proteomics was demonstrated.
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Experimental section
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Chemicals and reagents
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Water, methanol, propyl paraben, and three polycyclic aromatic hydrocarbon (PAH) standards (fluorene, anthracene, and benzo[a]pyrene) were purchased from Sigma-Aldrich (St.
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Louis, MO, USA). Acetonitrile (ACN) was purchased from Fisher Scientific (Pittsburgh, PA,
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USA). All solvents and chemicals were HPLC or analytical grade. Chromatographically purified
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bovine serum albumin (Sigma-Aldrich) ≥ 95% was prepared for bottom-up mass spectrometry
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analysis using a filter-aided sample preparation (FASP) technique.42 Approximately 500 µg of
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protein were loaded onto a 30 kDa cut-off ultra-filtration spin filter (Vivicon) for the FASP
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protocol. Due to the high concentration of the final BSA peptide mixture, it was diluted 100 or
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1000 fold and cleaned once more with a C-18 solid phase extraction cartridge (Sigma-Aldrich)
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prior to injection into the LC.
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Instrumentation
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The pumping system for the new gradient nano-flow UHPLC instrument (Figure 1) was
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engineered at VICI Valco Instruments (Houston, TX, USA). Compared to our previous gradient
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pumping system, several important modifications were made as follows: (1) the “Y” design (i.e.,
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two pumps and one valve) was changed to two individual pumps (each with stepper motor and
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high-pressure valve), which were connected to a separate injection valve (Figure 1); (2) a new
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proprietary sealing material was used to seal around the piston; and (3) smaller i.d. tubing was
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used to reduce the dwell volume. The “Y” design used a size 11 actuator, which could only hold
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up to 8,000 psi (550 bar) pressure, while the new design uses a size 17 actuator, which is more
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accurate and can hold much higher pressure.
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Overall, the pumping system included two pumps, each with its own high pressure valve
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and stepper motor, a three-way static mixing tee connected to a serpentine tube for solvent
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mixing, and another high pressure valve (18,000 psi) with a stop-flow injector. The pumping
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system weighed 5.9 kg (13 lbs) and could hold up to 1100 bar (16,000 psi) pressure. Each pump
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volume capacity was 30 µL. The stop-flow injector contained a sample groove in the rotor,with
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sample volume of 60 nL, or a 1 µL external sample loop; however, the groove or external sample
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loop could be engineered to deliver sample volumes anywhere between 5 nL and the 10 µL
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range. Zero dead-volume (360 µm) fittings especially designed for capillary columns were used
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for all connections, and no splitting was employed. This system provided accurate non-split flow
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in the low nanoliter to microliter per minute range (as described previously33), and was fully
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software-controlled. An on-column deep UV LED (260 nm) absorption detector described
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earlier,41 or an LTQ Orbitrap MS (described later in this section) was used for detection.
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System evaluation
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The methods used to determine the dwell volume and gradient step accuracy were
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reported earlier.31 In brief, methanol and propyl paraben in methanol were used as mobile phases
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A and B, respectively. A linear gradient was programmed through a hollow capillary (150 µm
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i.d.) from 0 to 100% B in 10 min with an isocratic hold at 100% B for several min. An injection
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of uracil was used to determine the capillary dead volume. The dwell volume of the system was
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calculated by subtracting the capillary dead volume from the gradient delay volume.
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For evaluating step accuracy, the system was programmed from 0% B to 100% B 10%
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intervals. The gradient was stopped every 10% step for several minutes to record the UV-
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absorption signal. The absorbance recorded by the detector increased as the proportion of B in
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the mobile phase increased, and reached a maximum at 100% B. Every measurement was
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repeated at least four times to determine the precision of the results. The recorded absorbance
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value at each step was divided by the absorbance recorded at 100% B, which served as a
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reference.
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Injection carry-over was studied by recording the signal obtained by first injecting uracil (0.33 mg/mL in an ACN/water mixture, 70:30 v/v). Then, the injector was thoroughly cleaned by
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purging with mobile phase, and a blank injection (mobile phase) was made. Isocratic elution was
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used (ACN/H2O, 70:30 v/v), and the flow rate was 2 µL/min. These experiments were repeated
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three times, and the detector signals were recorded. For each experiment, the peak area in the
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blank divided by the peak area of an analyte signal, multiplied by 100%, was reported as the
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percent carry-over.
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Chromatographic performance was evaluated using a packed capillary column
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(ACQUITY BEH130 C18, 1.7 µm, 100 mm × 150 µm i.d., Waters, Milford, MA) to separate a
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PAH mixture under gradient programming conditions. The post-column capillary was removed
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and replaced by a UV-transparent fused silica capillary (150 µm i.d.), which was used as a
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detection window. Gradient elution was programmed from 50% A to 100% B in 11.6 min.
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Solvent A was water and solvent B was ACN. The flow rate was 2 µL/min. The retention time
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reproducibilities (n = 4) of components were calculated.
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Coupling to an LTQ Orbitrap MS
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Polyimide coated fused silica tubing (75 µm i.d. × 365 µm o.d.) was used to prepare a
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column for coupling to the MS. Before packing, one end of the capillary was melted using a
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small butane micro torch, and pulled into a narrow tip (approximate 25 µm i.d.) to be used for
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electrospray ionization (ESI). Then, the capillary was packed with 1.7 µm BEH C18 particles
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(Waters, Milford, MA) by slurry packing. After the desired length (approximately 10 cm) was
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packed, the column was flushed with ACN before being used for MS analysis.
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A hollow capillary (25 µm i.d. × 365 µm o.d., 15 cm total) was used for the transfer line
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between the column with integrated ESI tip and injection valve. A VICI zero dead volume union
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was used to connect the transfer line and the column as well as to apply the high voltage for
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electrospray (photographs of all connections and column with integrated electrospray tip are
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shown in the Supplemental Information, Figures S1-S2). MS detection was carried out after ESI
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in the positive-ion full-scan mode. An LTQ Velos Pro-Orbitrap Elite tandem MS from Thermal
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Fisher (Waltham, MA USA) was used, and the settings of the MS were as follows: spray voltage,
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2.5 kV; capillary temperature, 325oC; and scan range, 150-2000 m/z. Nitrogen was used as
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sheath gas (3 arb. units). Data acquisition and analysis were performed using Thermo Xcalibur
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software Version 2.2.
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Results and discussion
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Pump operation
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The UHPLC system contained a four-port injection valve to switch between sample
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loading and injection (Figure 2). Each port served a specific purpose as described in the
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following: S is the sample injection port, W is the waste port, C is the column port, and M is the
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port through which the mixed mobile phase flowed to the internal sample groove and then to the
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column and detector. SG represents the sample groove in the rotor for loading the sample.
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Software controls the pump to switch automatically between the “load” and “inject”
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positions. In the load position, the pumps were automatically refilled with their respective mobile
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phases A and B at the preset rate of 20 µL/min through a 200 µm i.d. tube. At the same time, the
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sample was introduced manually into the 60 nL sample loop. After the valve was switched to the
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inject position (i.e., the rotor rotated by 90o), solvents from the pumps were mixed at the tee to
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form a gradient flow. Then this gradient flow was used to carry the sample in the sample loop
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through the analytical column to the detector for analysis.
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Dwell volume
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The dwell volume is defined as the volume from the solvent mixing point to the head of the analytical column.43 The sample experiences undesirable isocratic broadening in the dwell
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volume. When performing fast separations in LC, there are two main concerns related to large
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system dwell volume: (1) unreliable gradient method transfer between columns of different
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geometries, and (2) greater than expected separation time.21 Small dwell volume is highly
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recommended for fast analysis, especially when small i.d. columns are used, such as capillary
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columns. Knowing the dwell volume of a new system is also very critical for transferring
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methods from conventional LC to UHPLC.
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The dwell volume was calculated by subtracting the capillary dead volume from the
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gradient delay volume. The dead volume was 1.91 µL (1.91 min × 1.0 µL/min), so the dwell
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volume of this system was calculated to be 0.64 ± 0.008 µL. This value is less than half of the
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dwell volume measured for our previous nano-flow gradient system (1.3 µL),32 and less than the
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delay volume of a Waters NanoACQUITY UPLC system (< 1 µL).
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Gradient profile
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Good gradient accuracy and precision is a prerequisite for achieving reproducible
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separations. To test the accuracy of the gradient, experimental step errors were plotted against
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their corresponding theoretical step percentage values as illustrated in Figure 3A. Deviations
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from predicted values were less than 0.8%. A gradient step accuracy of ± 1% is considered to be
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acceptable for an LC system.32 In order to evaluate the precision of the gradient, experimental
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RSD values were calculated for a series of step percentages and plotted against their respective
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theoretical step percentages. As shown in Figure 3B, the RSD values (n = 4) were less than 0.6%,
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which is comparable to commercial instruments. Therefore, the gradient performance of this
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system was found to be excellent in terms of step accuracy and precision.
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Low carry-over is important for quantitative analysis in LC. Uracil was chosen as test analyte because a non-retained marker is commonly used to evaluate the injector performance.
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Data from this work showed that the nano-flow pump injector had low carry-over (0.20 ± 0.1%).
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This indicated that the flow-through injector is very reliable for quantitative work.
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Reproducible retention time is a fundamental requirement for chromatographic
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separations. Under gradient conditions, high reproducibility comes from high gradient accuracy.
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As shown in Figure 4, highly reproducible retention times of PAHs were obtained by using the
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UHPLC system. The RSD values were calculated to be less than 0.12%, which is better than the
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value (1.42%) obtained from our previous “Y” design gradient pumping system.32 Day-to-day
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reproducibility was also measured from experiments conducted over three days with three
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injections per day. The RSD was less than 0.17% for these PAH compounds. It should be noted
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that there was still some dead-volume between the column and UV detector, so separation
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performance could be further improved if this dead-volume was removed.
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Performance under high pressure and coupling with MS
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Another nano-flow UHPLC system with 1.0 µL sample loop was coupled to an LTQ
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Orbitrap MS for proteomic analysis. Due to the small particle size (1.7 µm) used in the analysis,
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higher backpressure (>10,000 psi) was required. Under high pressure, solvents compress to a
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certain extent, which leads to inaccurate flow rate and a distorted gradient. Most commercial
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pumping systems use reciprocating designs, while some use flow and pressure feedback control
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to deal with solvent compressibility. In our system, for simplicity, no flow and pressure sensors
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were employed.
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Therefore, in order to obtain the desired linear gradient, we evaluated two different ways
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to deal with solvent compressibility. In the first approach, at the beginning, both pumps were
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moved at the same speed until pressure was built up, and then the pump for solvent A (water)
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was programmed to pump at full speed while the other pump was temporarily stopped to wash
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all of solvent B (acetonitrile) out of the line. Sample was then injected into the flow stream and
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the elution gradient was started. Figure 3S in the Supplemental Information shows the gradient
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profile for operating the pumping system in this manner. After the point of sample injection, a
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near-linear gradient was generated. For the second approach, a series of gradient steps was
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generated at the first of the run to compensate for the solvent compressibility. As shown in
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Figure 5A, without an initial compensation procedure, the gradient was not linear, but jumped
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rapidly from 0 to 40% solvent B (uracil was added to solvent B for easy detection) with a steep
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slope at the beginning. By adding two gradient steps (gradient solvent B at 25% for 10 min and
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then 5% for 10 min), a near linear gradient from 5% to 40% was obtained as shown in Figure 5A.
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Both gradient compensation approaches were used to separate a trypsin-digested bovine
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serum albumin (BSA) sample. Using the method of delay injection, a 25 min gradient from 5%
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to 45% acetonitrile was used, for the chromatogram shown in Figure 5B. The FWHM peak width
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was approximately 10 s, the dwell volume was less than 2 µL, and an identified peptide coverage
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of over 90% was obtained using Mascot.44 Similar results were obtained using stepwise gradient
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compensation as shown in Figure 5C, with a gradient from 5% to 30% in 30 min and FWHM of
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approximately 15 s. Compared to commercial nano-flow LC systems that exhibit dwell times of
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over 10 min (> 4 µL in volume), peptide coverages of 67% to 87%, and peak widths (FWHM) of
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approximately 20 s (3-5 µm particles),45 the dwell time in our system was less than 4 min (using
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delayed injection), which improved the duty cycle better than 20%. Further work is currently
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being done to implement an initial solvent compression routine into the operating procedure.
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Conclusions
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Ultra-high operating pressures for capillary LC were made possible using a newly developed LC pumping system. This new nano-flow gradient system gave highly reproducible
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retention times of PAH compounds on a capillary column packed with sub-2 µm particles.
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Efficient gradient separation of peptides was also demonstrated when coupled to an LTQ
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Orbitrap MS. The features of the capillary nano-flow UHPLC system described in this study
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include: (1) it is simple to operate and maintain, (2) it consumes a minimum amount of solvent,
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(3) it is easy to position close to the electrospray source (which greatly reduces band broadening
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and analysis time, and improves detection limits), and (4) it provides high resolution LC of
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complex peptide mixtures for proteomics studies. Two simple approaches were demonstrated to
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address solvent compressibility during initial pressurization of the system for ultrahigh pressure
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operation.
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Supporting Information
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S1. Photographs of a column with integrated electrospray tip.
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S2. Photographs showing the interface between the nano-flow UHPLC system and
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Orbitrap MS. S3. Gradient profile obtained when both gradient pumps were initially moved at the same
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speed until pressure was built up, and then the pump for solvent A was programmed to pump at
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full speed while the other pump was temporarily stopped to wash solvent B out of the line.
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REFERENCES
299
(1) MacNair, J. E.; Lewis, K. C.; Jorgenson, J. W. Anal. Chem. 1997, 69, 983-989.
300
(2) MacNair, J. E.; Patel, K. D.; Jorgenson, J. W. Anal. Chem. 1999, 71, 700-708.
301
(3) Wu, N.; Lippert, J. A.; Lee, M. L. J. Chromatogr. A 2001, 911, 1-12.
302
(4) De Vos, J.; Broeckhoven, K.; Eeltink, S. Anal. Chem. 2016, 88, 262-278.
303
(5) Bouvier, E. S. P.; Koza, S. M. TrAC, Trends Anal. Chem. 2014, 63, 85-94. 13 ACS Paragon Plus Environment
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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
304 305
(6) Gumustas, M.; Kurbanoglu, S.; Uslu, B.; Ozkan, S. A. Chromatographia 2013, 76, 13651427.
306
(7) Denoroy, L.; Zimmer, L.; Renaud, B.; Parrot, S. J. Chromatogr. B 2013, 927, 37-53.
307
(8) Purcaro, G.; Moret, S.; Bučar-Miklavčič, M.; Conte, L. S. J. Sep. Sci. 2012, 35, 922-928.
308
(9) Kumar, A.; Saini, G.; Nair, A.; Sharma, R. Acta Pol. Pharm. 2012, 69, 371-380.
309
(10) Howard, J. W.; Kay, R. G.; Pleasance, S.; Creaser, C. S. Bioanalysis 2012, 4, 2971-2988.
310
(11) Broeckhoven, K.; Desmet, G. TrAC, Trends Anal. Chem. 2014, 63, 65-75.
311
(12) Jorgenson, J. W. Annu. Rev. Anal. Chem. 2010, 3, 129-150.
312
(13) Anspach, J. A.; Maloney, T. D.; Colón, L. A. J. Sep. Sci. 2007, 30, 1207-1213.
313
(14) Nováková, L.; Matysová, L.; Solich, P. Talanta 2006, 68, 908-918.
314
(15) Gritti, F.; Martin, M.; Guiochon, G. Anal. Chem. 2009, 81, 3365-3384.
315
(16) Gritti, F.; Guiochon, G. J. Chromatogr. A 2007, 1138, 141-157.
316
(17) Colón, L. A.; Cintrón, J. M.; Anspach, J. A.; Fermier, A. M.; Swinney, K. A. Analyst 2004,
317
129, 503-504.
318
(18) Tolley, L.; Jorgenson, J. W.; Moseley, M. A. Anal. Chem. 2001, 73, 2985-2991.
319
(19) Mazzeo, J. R.; D. Neue, U.; Kele, M.; Plumb, R. S. Anal. Chem. 2005, 77, 460 A-467 A.
320
(20) Fekete, S.; Schappler, J.; Veuthey, J. L.; Guillarme, D. TrAC, Trends Anal. Chem. 2014, 63,
321
2-13.
322
(21) Fekete, S.; Kohler, I.; Rudaz, S.; Guillarme, D. J. Pharm. Biomed. Anal. 2014, 87, 105-119.
323
(22) De Vos, J.; Broeckhoven, K.; Eeltink, S. Anal. Chem. 2016, 88, 262-278.
324
(23) Fekete, S.; Fekete, J. J. Chromatogr. A 2011, 1218, 5286-5291.
325
(24) Wu, N.; Bradley, A. C.; Welch, C. J.; Zhang, L. J. Sep. Sci. 2012, 35, 2018-2025.
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Analytical Chemistry
(25) Omamogho, J. O.; Hanrahan, J. P.; Tobin, J.; Glennon, J. D. J. Chromatogr. A 2011, 1218, 1942-1953. (26) Alexander, A. J.; Waeghe, T. J.; Himes, K. W.; Tomasella, F. P.; Hooker, T. F. J. Chromatogr. A 2011, 1218, 5456-5469. (27) Gritti, F.; Sanchez, C. A.; Farkas, T.; Guiochon, G. J. Chromatogr. A 2010, 1217, 30003012.
332
(28) Swartz, M. E. J. Liq. Chrom. Relat. Tech. 2005, 28, 1253-1263.
333
(29) Jorgenson, J. W.; Guthrie, E. J. J. Chromatogr. A 1983, 255, 335-348.
334
(30) Waters product literature.
335
(31) Baram, G. I. J. Chromatogr. A 1996, 728, 387-399.
336
(32) Sharma, S.; Plistil, A.; Barnett, H. E.; Tolley, H. D.; Farnsworth, P. B.; Stearns, S. D.; Lee,
337 338 339 340 341
M. L. Anal. Chem. 2015, 87, 10457-10461. (33) Sharma, S.; Plistil, A.; Simpson, R. S.; Liu, K.; Farnsworth, P. B.; Stearns, S. D.; Lee, M. L. J. Chromatogr. A 2014, 1327, 80-89. (34) Sharma, S.; Tolley, L. T.; Tolley, H. D.; Plistil, A.; Stearns, S. D.; Lee, M. L. J. Chromatogr. A 2015, 1421, 38-47.
342
(35) Zhou, L.; Lu, J. J.; Gu, C.; Liu, S. Anal. Chem. 2014, 86, 12214-12219.
343
(36) Snyder, D. T.; Pulliam, C. J.; Ouyang, Z.; Cooks, R. G. Anal. Chem. 2016, 88, 2-29.
344
(37) Aebersold, R.; Mann, M. Nature 2003, 422 (6928), 198-207.(38) Shen, Y. F.; Zhao, R.;
345
Belov, M. E.; Conrads, T. P.; Anderson, G. A.; Tang, K. Q.; Pasa-Tolic, L.; Veenstra, T. D.;
346
Lipton, M. S.; Udseth, H. R.; Smith, R. D. Anal. Chem. 2001, 73 (8), 1766-1775.
347 348
(39) Iwasaki, M.; Sugiyama, N.; Tanaka, N.; Ishihama, Y. J. Chromatogr. A 2012, 1228, 292297.
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(40) Li, S.; Hao, Q.; Gounarides, J.; Wang, Y. K. J. Mass Spectrom. 2012, 47, 1074-1082.
350
(41) Sharma, S.; Tolley, H. D.; Farnsworth, P. B.; Lee, M. L. Anal. Chem. 2015, 87, 1381-1386.
351
(42) Wisniewski, J. R.; Zougman, A.; Nagaraj, N.; Mann, M., Nature methods 2009, 6 (5), 359-
352
62
353
(43) Li, Y.; Tolley, H. D.; Lee, M. L. J. Chromatogr. A 2011, 1218,1399−1408.
354
(44) Perkins, D. N.; Pappin, D. J. C.; Creasy, D. M.; Cottrell, J. S. Electrophoresis 1999, 20,
355 356 357
3551-3567. (45) Liu, Q.; Cobb, J. S.; Johnson, J. L.; Wang, Q.; Agar, J. N. J. Chromatogr. Sci. 2014, 52, 120-127.
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Figure captions
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Figure 1. (A) Cut-away drawing of a single nano-flow pump; (B) photograph of the nano-flow
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UHPLC with LED detector.
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Figure 2. Operating schematics of the nano-flow UHPLC injection valve. (A) Load position, and
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(B) inject position.
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Figure 3. (A) Gradient step accuracy (±% solvent B) and (B) precision in gradient step accuracy.
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Figure 4. Reproducibility in retention times of of PAHs.
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Figure 5. (A) Comparison of gradient profiles (uracil was added to monitor the concentration of
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solvent B, acetonitrile); blue: no compensation step with pump speed set to generate a linear
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gradient from 0% to 40%; red: two step manual compensation, 10 min at 25% B and then 10 min
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at 5% B, was used prior to starting the sample elution gradient. (B and C) Chromatograms of a
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trypsin-digested BSA sample using coupled UHPLC-Orbitrap MS: (B) sample injected 20 min
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after 10 min 50:50 (A/B, water/ACN) and 10 min 95:5 wash (total ion and extracted-ion
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chromatograms, m/z = 632. (C) Sample injected at 0 min, compensation steps of 75:25
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(water/CAN) for 10 min and 95:5 for 10 min before linear gradient of 5% to 30% was started
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(total-ion and extracted-ion chromatograms, m/z = 654. Experimental conditions: column with
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integrated ESI tip, 12 cm (75 µm i.d. × 365 µm o.d.); mobile phase A, 0.1% formic acid in
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water/ACN (95:5, v/v); mobile phase B, 0.1% formic acid in ACN; flow rate at 500 nL/min;
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injection volume, 1.0 µL.
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Figure 1
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Figure 2
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