Optimization of Fiber Coating Structure Enables Direct Immersion

(2) SPME addresses the need to facilitate rapid sampling. ... used for DI-SPME-GC analysis of pesticides from fruits and vegetables after sample dilut...
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Technical Note

Optimization of Fibre Coating Structure Enables Direct Immersion Solid Phase Microextraction and High Throughput Determination of Complex Samples Janusz Pawliszyn, and Erica Silva Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/ac301305u • Publication Date (Web): 25 Jul 2012 Downloaded from http://pubs.acs.org on July 26, 2012

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Analytical Chemistry

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Optimization of Fibre Coating Structure Enables

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Direct Immersion Solid Phase Microextraction and

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High Throughput Determination of Complex

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Samples

5 6 7 8 9

Érica A. Souza Silva and Janusz Pawliszyn*

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Department of Chemistry, University of Waterloo, Ontario, N2L 3G1, Canada

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*Corresponding author: [email protected]

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ABSTRACT

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This study presents a new approach for improving the structure, and hence the

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robustness, of the SPME fibre coating applied for GC analysis. It involves application of

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an external layer of PDMS over the commercial PDMS/DVB extraction phase. The fibre

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provided extraction capabilities similar to that exhibited by the original PDMS/DVB fibre

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towards triazole pesticides from water samples. Furthermore, the fibre could be utilized

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for over 100 extractions in direct contact with a complex food matrix such as whole grape

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pulp, with no sample pre-treatment required. The amount of extracted pesticides from

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whole

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extraction/desorption/conditioning cycles which is a dramatic improvement when

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compared to commercial PDMS/DVB fibre coating applied in food analysis facilitating

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high throughput automation.

grape

pulp

had

RSD

values

below

20

%

throughout

130

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Analytical Chemistry

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INTRODUCTION

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Recently there has been growing effort towards the development and improvement of

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sample preparation methods for simple and fast analysis of complex matrices. Such a

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situation has forced analysts to develop better, less labour-intensive, faster and more

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accurate analytical procedures in different fields such as biological, food and

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environmental analysis.1

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In the early 1990’s Pawliszyn and co-workers developed solid-phase microextraction

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(SPME), which integrates sampling, extraction, concentration and sample introduction

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into a single solvent-free step.2 SPME addresses the need to facilitate rapid sampling.

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However, the appropriate selection of the extraction coating is one of the most critical

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steps in SPME method development. The suitability of the coating for a specific analyte

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of interest is determined by the polarity of the coating and its selectivity towards the

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analytes in contrast to other matrix components.3 Given the great diversity of analyte-

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matrix combinations, significant developments are still being made in some critical areas.

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For instance, due to the complex nature of matrices, direct immersion (DI-SPME) can be

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difficult, and some pretreatment or clean-up of the sample prior to SPME extraction may

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be necessary to protect the coating and avoid the fouling of the extraction phase. Fouling

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is caused by irreversible adsorption of macromolecules from the complex matrix at the

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coating surface which could lead not only to a substantial decrease in the fibre lifetime,

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making it unusable for more than a few samples, but could also change the coating

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extraction properties.4

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Therefore, the search for new coatings to improve the performance of DI-SPME coupled

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to GC analysis in complex matrices is an active research topic.5-6. In spite of the

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drawbacks presented by the commercially available coatings, those are still a first choice

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for routine and inter-laboratory validations. Even though PDMS is preferred for the

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extraction of nonpolar pesticides, it has been extensively used for the extraction of a wide

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range of analytes in complex matrices.7-8 The main premise supporting this fact is that

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PDMS, as a non-porous liquid coating, suffers less from the irreversible fouling effect

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caused by the matrix components when compared to solid coatings. PDMS coating is the

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most robust option for directly analyzing complex matrices, making it preferred

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regardless of the sensitivity of this coating towards the analytes of interest. Jahnke et al.

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corroborate this hypothesis in a recent publication investigating the effects of non-volatile

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matrix macromolecules fouling the PDMS, concluding that the sorptive properties of the

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PDMS were not modified, and that PDMS is suitable for sampling of highly complex

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matrices.9 Moreover, the authors mentioned that fouling of the PDMS might still occur in

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highly complex matrices, but a physical cleaning of the polymer is sufficient to

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circumvent this problem.

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Additionally, PDMS/DVB fibre coating has also been extensively used for DI-SPME-GC

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analysis of pesticides from fruits and vegetables after sample dilution. This coating

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presents increased retention capacity, high distribution coefficient, smaller diffusion

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coefficient, and high selectivity.8,10 However, it suffers of irreversible fibre fouling

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damage when placed in direct contact to the matrix. This can be very problematic as it

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can change the chemistry of the coating, thus affecting the uptake of the analyte and the

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reproducibility of extraction, resulting in poor accuracy and decreasing extraction

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efficiency of the fibre upon repeated use.11-12

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All aforementioned limitations, together with our experimental findings, motivated us to

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explore the possibility of modifying existing commercial SPME fibre coatings with a thin

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layer of PDMS to create a new type of SPME fibre, achieving matrix-compatibility while

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retaining the original coating sensitivity towards the analytes of interest, for GC analysis

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of complex samples. In the present study, grapes were chosen as a model of complex

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matrix, and triazole pesticides, which are vastly applied in vineyards, were chosen as

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model analytes. The modified SPME fibre was tested for extraction efficiency and

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robustness when directly subjected to grape matrix.

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EXPERIMENTAL SECTION

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Chemicals and Materials

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Triazole pesticides standards (triadimefon, penconazole, triadimenol, hexaconazole and

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diniconazole) were Pestanal grade purchased from Sigma-Aldrich (Oakville, ON,

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Canada). Individual solutions (c.a. 20 mg/mL) of each pesticide were prepared in

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methanol. A mixture standard stock solution was prepared containing 2000 mg/L of each

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pesticide in methanol. Different working standards solutions (0.1 to 200 ng/µL of each

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pesticide) were prepared by dilution in the same solvent.

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Sylgard 184 (PDMS prepolymer and curing agent) was purchased from Dow Corning

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(Midland, MI, USA). Commercial SPME fibres (PDMS 100µm, PDMS/DVB 65µm)

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were purchased from Supelco (Bellefonte, PA, USA).

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GC Analysis

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Analysis of triazole pesticides was performed on a Varian Saturn 3800 GC/2000 ITMS

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system fitted with a HP-5MS column (30 m, 0.25 mm i.d., 0.25 µm film thickness)

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(Hewlett-Packard, Avondale, PA). Helium as the carrier gas was set to 1.5 mL/min. The

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1079 injector was set to at a temperature of 260 °C (unless otherwise specified). The

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column temperature program was initially set at 70 °C for 2 min, ramped at 40 °C/min to

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235 °C for 1 min, ramped at 3 ºC/min to 250 ºC and then ramped at 40 ºC/min to 280 ºC

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and held for 12.12 min giving a total run time of 24 min. For water samples analysis, the

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ion trap was operated in full scan mode (MS), whereas, for the grape pulp matrix the

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analyzer was operated in tandem mode (MS/MS). The MS operational conditions were as

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follows: electron ionization (EI) was always 70 eV; temperatures of 180, 50 and 260 °C

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for the trap, manifold and transfer line respectively; initially a mass range of 55-325 m/z

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was scanned to confirm the retention times of analytes. The multiplier voltage (1x105

105

gain) was 1600 V with a multiplier offset of +200V. Automatic gain control (AGC) was

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turned on with an AGC target value of 20,000 counts for EI-MS and 2000 counts for EI-

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MS/MS; the emission current was 10 µA for MS and 80 µA for MS/MS. For MS/MS, the

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AGC pre-scan ionization time was 1500 µs and the isolation window was 3m/z (except

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for diniconazole where a 5 m/z window was used). All specific MS/MS conditions for the

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studied triazole pesticides are listed in Supplementary Information Table S1. Automated

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analysis was performed using a CTC CombiPal autosampler (Zwingen, Switzerland)

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using the associated Cycle Composer software (Version 1.4.0). The PAL was equipped

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with a SPME fibre holder, a temperature controlled six-vial agitator tray, and a fibre-

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conditioning device.

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Preparation of PDMS-modified fibre

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Sylgard 184® PDMS pre-polymer and curing agent were mixed at a 10:1 ratio, according

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to the manufacturer’s manual, into a polypropylene centrifuge tube and subjected to

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centrifugation for 3 min at 4000 rpm for degassing. The coating procedure consisted of

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immersing the commercial PDMS/DVB fibre into the PDMS solution and subsequently

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pulling out at a slow rate of approximately 0.5 mm s-1. Passing it through a micropipette

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tip of about 350 µm diameter aperture ensured that a thinner layer was formed, with the

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excess polymer being removed. After the coating process, the coated fibre was placed in

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a vacuum oven at 50 ºC under N2 flow for 12 hrs. The coating/curing process was

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repeated twice to assure complete and uniform coverage. Prior to use the fibre was

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conditioned in a GC injection port (PTV) under helium flow from 100 ºC (hold for 5 min)

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to 250 ºC (hold for 30 min) at 5 ºC/min. The fibre was then conditioned again at 250 ºC

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for 10 min. The 10-min conditioning cycle was repeated a few more times until a stable

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GC baseline was obtained.

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After curing and conditioning, the modified coatings were inspected using optical stereo

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microscope to ensure that a thin layer of smooth surface was achieved. In order to verify

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the topography of the coating surface as well as the thickness of the PDMS outer layer,

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scanning electron microscopy (SEM) images were acquired using an LEO 1530 field

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emission (Carl Zeiss NTS GmbH, Germany).

134 135

SPME procedure

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Triazoles determination in grapes

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Uncontaminated white grapes, purchased at a local market in Waterloo (ON Canada),

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were manually stemmed, washed with de-ionized water, dried, and crushed using a

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blender. A sample aliquot (9 g) was weighed in a 10-mL vial, fortified at 100 ng g-1. A 5

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min incubation of the sample was performed in the autosampler agitation unit at 500 rpm

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and at 30°C, followed by a 30 min extraction at 30ºC, while stirring at 500 rpm.

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Following extraction, the fibre was rinsed in DI water at 30 ºC while stirring at 500 rpm

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in the autosampler agitator unit for 50 s. Subsequently, the fibre was placed in the GC

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injection port for desorption for 7 min at 260 ºC.

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Analytical Chemistry

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Triazoles determination in water

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This approach was employed to compare the extraction kinetics between the commercial

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PDMS/DVB fibre and the PDMS-modified fibre. An aliquot of 18 mL of an aqueous

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solution containing c.a. 5.5 ng mL-1 of each triazole was placed in a 20-mL vial. A 5 min

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incubation of the sample was performed in the stir plate while stirring at 1200 rpm and at

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30 °C. Extraction time ranged from 5 min to 1440 min. Following extraction, the fibre

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was placed in the GC injection port for desorption for 7 min at 260 ºC. All extraction

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time points were performed in duplicate.

154 155

RESULTS AND DISCUSSION

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Initial Assessment: Commercial PDMS/DVB fibre coating

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In an attempt to overcome the problem with irreversible fibre fouling, a rapid rinsing of

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the fibre in de-ionized water after extraction and prior to desorption was implemented. It

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was observed that no significant loss of analyte occurred up to 50 s of rinsing, thus, it was

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chosen for further experiments. Subsequently, grape samples were subjected to extraction

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applying a 50 s rinsing prior to desorption. Overall, the obtained results demonstrate an

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ineffectual improvement in the fibre lifetime. In agreement with De Jager et al.12, after 20

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extraction/desorption cycles in grape matrix the PDMS/DVB fibre was blackened and a

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substantial decrease in extraction efficiency was observed, resulting in very

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irreproducible results. After 10 extractions, the extraction efficiency had decreased by 3

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to 41% and by the 20th extraction, the efficiency had dropped by 83 to 89%. The same

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experimental set up was repeated for PDMS fibre to evaluate the performance of PDMS

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coating, since the ability of PDMS to withstand complex matrix without changes in its

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sorptive properties has been subject to study.9 The results obtained for both sets of

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experiments are shown in Figure 1. Responses were normalized taking first extractions as

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100 %. The results for PDMS coating indicated that, after 20 extractions, the extraction

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efficiency had dropped by 8 to 14 %. Indeed, PDMS coating offered improved

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repeatability and robustness to direct immersion in complex matrix, despite its low

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sensitivity towards the studied analytes. Therefore, at this point the question of sacrificing

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sensitivity for robustness and vice-versa arises. Nevertheless, in the present work, a new

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approach is attempted, in which the benefits of the high sensitivity exhibited by the

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PDMS/DVB and the robustness of PDMS are combined.

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Analytical Chemistry

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Figure 1.Repeatability of commercial fibres in grape matrix (20 extraction cycles using a

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single fibre). (A) PDMS/DVB 65 µm; (B) PDMS 100 µm. Normalization performed

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taken extraction efficiency of first extraction for each analyte as 100 %. Extractions were

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peformed for 30 min at 30 ºC, from 9 g grape pulp with triazole pesticides at a

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concentration of 100 ng g-1.

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PDMS-modified coating preparation and characterization

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It was necessary to optimize the coating method (spraying or dipping) and the overall

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parameters such as addition of solvent, rate of pulling and aperture diameter. The

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spraying method resulted in highly irregular coatings, thus, the work proceeded using

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dip-coating. The optimized procedure is presented in the experimental section. The

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optimized PDMS outer layer was obtained for two layers of PDMS which resulted in

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optimum surface coverage of the original coating. The study showed that thinner coatings

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(1 layer) did not ensure total surface coverage, resulting in a coating that still exhibited a

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porous surface. In addition, thicker coatings (3 layers) resulted in non-uniform surface

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coverage in terms of thickness throughout the coating length and also rendering weaker

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physical stability due to excessive thickness that could lead to stripping of the coating

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when withdrawn inside the fibre needle. Figure 2 shows the SEM images of the coatings

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after being covered with a 10 nm layer of gold on its surface. The SEM image shows the

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formation of a thin PDMS film on the surface of the PDMS/DVB fibre. The image

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presents a uniform, non-porous, and smooth surface throughout the coating. The PDMS

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outer layer thickness for the optimized coating was estimated to be approximately 25-30

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µm.

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In order to investigate the reproducibility of the optimized overcoating procedure, the

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intra-fibre (n=4), as well as the inter-fibre reproducibility (three fibres, 3 replicates each)

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in both water and grape pulp matrices were found to be very good as indicated by R.S.D.

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values ranging from 0.1 to 11.4%. The results obtained are summarized in Supplementary

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Information Table S2.

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Figure 2.SEM image of the PDMS-modified coating (2 layers): Surface morphology and

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estimation of coating thickness using 900x magnification.

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Triazoles Extraction

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At first, DI-SPME of triazole compounds from water matrix was used to evaluate the

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effect of the external PDMS layer on extraction capabilities of the PDMS/DVB coating

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by comparing its extraction time profiles with those obtained with commercial

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PDMS/DVB 65 µm fibre. Profiles of extraction obtained with the PDMS-modified fibre

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shown in Figure 3 resulted very similarly for all the triazole pesticides studied. This is

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compared to non-modified PDMS/DVB fibre, where only marginal differences could be

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observed at shorter extraction times as a result of the additional step of diffusion of the

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analytes through the PDMS outer layer. Such an effect is better illustrated in

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Supplementary Information Figure S1, where it can be noted that the slopes of the initial

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stage of the adsorption profiles for triazole pesticides were only slightly decreased for

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PDMS overcoated fibre as compared to the non-modified fibre coating. However,

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statistical analysis of both extraction time profiles by means of t-test indicates that the

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kinetics of extraction was not influenced, by the additional barrier. Therefore, in the

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studied matrix-analyte-coating system, the diffusion through the thin PDMS outer layer

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does not statistically reduces the rate of mass transfer even at pre-equilibrium extraction

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times. From a practical point of view, the obtained results are of utmost importance,

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since most SPME applications are performed in pre-equilibrium conditions. In the present

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work, the application of such modified coating in pre-equilibrium conditions does not

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jeopardize the overall sensitivity towards triazoles that would be achieved by the

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commercial PDMS/DVB coating. Additionally, as Figure 3 illustrates, the amount of

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analyte extracted at equilibrium or near equilibrium by the PDMS-modified coating is

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statistically equal to the amount extracted by the commercial PDMS/DVB. Moreover, the

234

results obtained suggest that there was no blockage of the extraction sites on the surface

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of the original PDMS/DVB coating by the additional PDMS layer, thus, no impairing of

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extraction capabilities of the original coating. In the present study, it seems that the

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PDMS layer does not substantially change either kinetic or thermodynamic parameters

238

associated with the original coating.

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It is worth emphasize that in this new configuration, the analytes after crossing the

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boundary layer present in the matrix must first diffuse through the PDMS overcoating

241

prior to the adsorption in the solid DVB coating. Since this in-between phase is a liquid

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polymer, if the distribution constant for a given analyte is substantially lower as

243

compared to DVB phase, the mass transfer is considerably slowed down, which can limit

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in some cases the kinetics of the extraction process (i.e. short extraction times

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applications). The reduction in the rate of mass transfer is dependent on the thickness of

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the overcoating, as well as on the differences in the distribution constant between the

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overcoated polymer and the extraction polymer. Therefore, according to SPME

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fundamentals, one might expect that different behaviors could be obtained for thicker

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PDMS outer layer as well as for analytes bearing different physical-chemical properties

250

(i.e. Log P values).

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252 253

Figure 3.Comparative extraction time profiles for triazoles pesticides using commercial

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PDMS/DVB fibre and PDMS/DVB/PDMS fibre. (A) Full extraction time profile (up to

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24h). (B) Shorter range extraction time profile (up to 1h). DI-SPME performed in 18 mL

256

nanopure water (n=2) at 5.5 ng mL-1.

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Analytical Chemistry

257

Fibre life-time

258

The stability of the coatings over time is yet another practical parameter of top

259

importance in SPME technique. To determine endurance and reusability, the modified

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PDMS/DVB/PDMS fibre was subjected to a series of 130 successive DI-SPME cycles in

261

whole grape pulp. Each cycle consisted of 15 min extraction at 30 ºC; 50 s rinsing in de-

262

ionized water prior to desorption; 7 min desorption at 260 ºC; post-desorption washing in

263

de-ionized water for 2.5 min; and 2.5 min fibre conditioning at 250ºC in the autosampler

264

conditioning station device. In the present experiment, the fibre was constantly inspected

265

under electronic microscope (every 10 cycles) and, when needed, manually freed of any

266

possible debris attached to its surface by simply using a KimWipe® tissue. No

267

irreversible damage on the surface was observed. Moreover, quality control (QC)

268

consisting of water samples spiked with triazole pesticides were distributed along the

269

batch to ensure that the fibre performance was not altered.

270

As presented in Figure 4, the fibre endurance measured as the amount of analyte

271

extracted presented RSDs below 20%, which taking into account the complexity of the

272

studied matrix, is an impressive achievement with performance much superior to that

273

exhibited by the original commercial fibre, which exhibited over 80% drop in signal by

274

the 20th extraction. It is also worth noting that the amount of analyte extracted by SPME

275

is proportional to the free (unbound) concentration of analyte in the sample matrix. In

276

addition, in the present study a short pre-equilibrium extraction time was employed,

277

hence the small amount of absolute recoveries observed for all analytes. If sensitivity is

278

an issue, this can be overcome by applying longer extractions time. In terms of

279

reusability, due to the very complex matrix, there was a drop in the amount extracted

280

after the 90th extraction, but the amount extracted remained reproducible from the 90th to

281

the 130th extraction for most of analytes. Only one triazole pesticide (triadimefon)

282

exhibited pronounced variations throughout this study. One possible explanation for this

283

behaviour could be the fact that triadimefon can undergo biotransformation in rich

284

organic matter media. Moreover, it is expected that by employing the right calibration

285

technique, i.e. the use of internal standard to compensate for any possible variation in the

286

method, the newly developed coating could be easily reusable over 100 times in complex

287

food matrices such as whole grape pulp.

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It should also be noted that an accumulation of high molecular pigments compounds on

289

the inner DVB phase, causing discoloration of this phase, was observed along the slight

290

trend down on the extraction efficiency.

291

Finally, the improvement achieved by the newly modified coating is illustrated in Figure

292

5. Microscope pictures of both fibres before extraction from grape pulp, as well as SEM

293

pictures of surface morphologies for commercial PDMS/DVB coating fibre and PDMS-

294

modified coating fibre are presented. The extent of fouling on the surface of the coating is

295

dramatically reduced by the application of the PDMS outer layer, as presented in Figure

296

5.

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2.5

2 Absolute recovery (%)

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Analytical Chemistry

1.5

Triadimefon (14.2%) Penconazole (13.4%)

1

Triadimenol (14.0%) Hexaconazole (14.3%) Diniconazole (10.8%)

0.5

0 0

20

40

60 80 Extraction #

100

120

140

297 298

Figure 4.Robustness of the PDMS/DVB/PDMS fibre in DI-SPME mode in grape pulp

299

for studied triazole pesticides. DI-SPME performed in 9 g of whole grape pulp (130

300

extractions using a single fibre) at 100 ng g-1. Numbers in brackets and solid lines

301

represent the pooled R.S.D. (%) values and average values over the 130 extractions,

302

respectively.

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A

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Figure 5. Microscope picture of the commercial PDMS/DVB coating before extractions

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(A); Microscope picture of the PDMS/DVB/PDMS coating before extractions (B); SEM

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images of the PDMS/DVB coating after 20 extractions cycles in grape (C); and

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PDMS/DVB/PDMS coating after over 130 extractions cycles in grape (D). SEM surface

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morphology using 580x magnification.

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Analytical Chemistry

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CONCLUSIONS

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A new concept of modified SPME fibre coating suitable for direct immersion in complex

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matrix is presented. A procedure for preparing the new modified fibre was developed.

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Subsequently, its extraction capabilities towards triazole pesticides from water samples

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were proven to be similar to those exhibited by the original commercial PDMS/DVB

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coating. In the present study, the PDMS layer has not substantially changed the kinetic

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and thermodynamic parameters associated with the original coating for the target

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analytes. At the same time, the results show that modified PDMS/DVB/PDMS coating

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provides enhanced robustness in a highly complex matrix such as whole grape pulp when

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compared to the original commercially available PDMS/DVB. It is here demonstrated

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that it is possible to perform automated DI-SPME in a complex matrix such as whole

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grape pulp for over 100 extractions using a single fibre without the use of any sample

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pre-treatment. The practical aspects of the PDMS-modified coating demonstrated here

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create new opportunities for the application of DI-SPME-GC in analysis of complex

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samples not only laboratory high throughput, but also in-vivo determinations. The

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creation of perfectly smooth, uniform, non-fouling surfaces is one of the major

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prerequisites for high-throughput food applications, and to date, no commercially

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available fibre is suitable for such applications. Further investigation of the PDMS-

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modified coating capabilities towards analytes bearing different physical-chemical

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properties from food matrices of varied compositions, as well as research into the

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manufacturing of coatings with different outer layer chemistries and thicknesses is

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currently ongoing with the aims to better understand the kinetics and thermodynamic

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parameters involved in the application of such coatings, as well as improve the robustness

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in complex food and biological matrices.

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ACKNOWLEDGMENTS

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The authors thank the Natural Sciences and Engineering Research Council of Canada

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(NSERC), Agilent Technologies Foundation and Sigma-Aldrich Corporation for the

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financial support. The help of Dr. Viorica Lopez-Avila was also greatly appreciated in

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this research.

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REFERENCES

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(3) Risticevic, S.; Lord, H.; Górecki, T.; Arthur, C. L.; Pawliszyn, J. Nat. Protoc. 2010,

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E. J. Chromatogr. A 2010, 1217, 2533-2542.

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Analytical Chemistry

For TOC only

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