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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
4
Samples
5 6 7 8 9
Érica A. Souza Silva and Janusz Pawliszyn*
10 11
Department of Chemistry, University of Waterloo, Ontario, N2L 3G1, Canada
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*Corresponding author:
[email protected] 1 ACS Paragon Plus Environment
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ABSTRACT
15
This study presents a new approach for improving the structure, and hence the
16
robustness, of the SPME fibre coating applied for GC analysis. It involves application of
17
an external layer of PDMS over the commercial PDMS/DVB extraction phase. The fibre
18
provided extraction capabilities similar to that exhibited by the original PDMS/DVB fibre
19
towards triazole pesticides from water samples. Furthermore, the fibre could be utilized
20
for over 100 extractions in direct contact with a complex food matrix such as whole grape
21
pulp, with no sample pre-treatment required. The amount of extracted pesticides from
22
whole
23
extraction/desorption/conditioning cycles which is a dramatic improvement when
24
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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INTRODUCTION
27
Recently there has been growing effort towards the development and improvement of
28
sample preparation methods for simple and fast analysis of complex matrices. Such a
29
situation has forced analysts to develop better, less labour-intensive, faster and more
30
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
33
(SPME), which integrates sampling, extraction, concentration and sample introduction
34
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
36
steps in SPME method development. The suitability of the coating for a specific analyte
37
of interest is determined by the polarity of the coating and its selectivity towards the
38
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
41
difficult, and some pretreatment or clean-up of the sample prior to SPME extraction may
42
be necessary to protect the coating and avoid the fouling of the extraction phase. Fouling
43
is caused by irreversible adsorption of macromolecules from the complex matrix at the
44
coating surface which could lead not only to a substantial decrease in the fibre lifetime,
45
making it unusable for more than a few samples, but could also change the coating
46
extraction properties.4
47
Therefore, the search for new coatings to improve the performance of DI-SPME coupled
48
to GC analysis in complex matrices is an active research topic.5-6. In spite of the
49
drawbacks presented by the commercially available coatings, those are still a first choice
50
for routine and inter-laboratory validations. Even though PDMS is preferred for the
51
extraction of nonpolar pesticides, it has been extensively used for the extraction of a wide
52
range of analytes in complex matrices.7-8 The main premise supporting this fact is that
53
PDMS, as a non-porous liquid coating, suffers less from the irreversible fouling effect
54
caused by the matrix components when compared to solid coatings. PDMS coating is the
55
most robust option for directly analyzing complex matrices, making it preferred
56
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
62
circumvent this problem.
63
Additionally, PDMS/DVB fibre coating has also been extensively used for DI-SPME-GC
64
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
66
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.
79 80
EXPERIMENTAL SECTION
81
Chemicals and Materials
82
Triazole pesticides standards (triadimefon, penconazole, triadimenol, hexaconazole and
83
diniconazole) were Pestanal grade purchased from Sigma-Aldrich (Oakville, ON,
84
Canada). Individual solutions (c.a. 20 mg/mL) of each pesticide were prepared in
85
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
87
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
89
(Midland, MI, USA). Commercial SPME fibres (PDMS 100µm, PDMS/DVB 65µm)
90
were purchased from Supelco (Bellefonte, PA, USA).
91 92
GC Analysis
93
Analysis of triazole pesticides was performed on a Varian Saturn 3800 GC/2000 ITMS
94
system fitted with a HP-5MS column (30 m, 0.25 mm i.d., 0.25 µm film thickness)
95
(Hewlett-Packard, Avondale, PA). Helium as the carrier gas was set to 1.5 mL/min. The
96
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
99
and held for 12.12 min giving a total run time of 24 min. For water samples analysis, the
100
ion trap was operated in full scan mode (MS), whereas, for the grape pulp matrix the
101
analyzer was operated in tandem mode (MS/MS). The MS operational conditions were as
102
follows: electron ionization (EI) was always 70 eV; temperatures of 180, 50 and 260 °C
103
for the trap, manifold and transfer line respectively; initially a mass range of 55-325 m/z
104
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
106
turned on with an AGC target value of 20,000 counts for EI-MS and 2000 counts for EI-
107
MS/MS; the emission current was 10 µA for MS and 80 µA for MS/MS. For MS/MS, the
108
AGC pre-scan ionization time was 1500 µs and the isolation window was 3m/z (except
109
for diniconazole where a 5 m/z window was used). All specific MS/MS conditions for the
110
studied triazole pesticides are listed in Supplementary Information Table S1. Automated
111
analysis was performed using a CTC CombiPal autosampler (Zwingen, Switzerland)
112
using the associated Cycle Composer software (Version 1.4.0). The PAL was equipped
113
with a SPME fibre holder, a temperature controlled six-vial agitator tray, and a fibre-
114
conditioning device.
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Preparation of PDMS-modified fibre
116
Sylgard 184® PDMS pre-polymer and curing agent were mixed at a 10:1 ratio, according
117
to the manufacturer’s manual, into a polypropylene centrifuge tube and subjected to
118
centrifugation for 3 min at 4000 rpm for degassing. The coating procedure consisted of
119
immersing the commercial PDMS/DVB fibre into the PDMS solution and subsequently
120
pulling out at a slow rate of approximately 0.5 mm s-1. Passing it through a micropipette
121
tip of about 350 µm diameter aperture ensured that a thinner layer was formed, with the
122
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
124
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)
126
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
128
GC baseline was obtained.
129
After curing and conditioning, the modified coatings were inspected using optical stereo
130
microscope to ensure that a thin layer of smooth surface was achieved. In order to verify
131
the topography of the coating surface as well as the thickness of the PDMS outer layer,
132
scanning electron microscopy (SEM) images were acquired using an LEO 1530 field
133
emission (Carl Zeiss NTS GmbH, Germany).
134 135
SPME procedure
136
Triazoles determination in grapes
137
Uncontaminated white grapes, purchased at a local market in Waterloo (ON Canada),
138
were manually stemmed, washed with de-ionized water, dried, and crushed using a
139
blender. A sample aliquot (9 g) was weighed in a 10-mL vial, fortified at 100 ng g-1. A 5
140
min incubation of the sample was performed in the autosampler agitation unit at 500 rpm
141
and at 30°C, followed by a 30 min extraction at 30ºC, while stirring at 500 rpm.
142
Following extraction, the fibre was rinsed in DI water at 30 ºC while stirring at 500 rpm
143
in the autosampler agitator unit for 50 s. Subsequently, the fibre was placed in the GC
144
injection port for desorption for 7 min at 260 ºC.
145
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Analytical Chemistry
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Triazoles determination in water
147
This approach was employed to compare the extraction kinetics between the commercial
148
PDMS/DVB fibre and the PDMS-modified fibre. An aliquot of 18 mL of an aqueous
149
solution containing c.a. 5.5 ng mL-1 of each triazole was placed in a 20-mL vial. A 5 min
150
incubation of the sample was performed in the stir plate while stirring at 1200 rpm and at
151
30 °C. Extraction time ranged from 5 min to 1440 min. Following extraction, the fibre
152
was placed in the GC injection port for desorption for 7 min at 260 ºC. All extraction
153
time points were performed in duplicate.
154 155
RESULTS AND DISCUSSION
156
Initial Assessment: Commercial PDMS/DVB fibre coating
157
In an attempt to overcome the problem with irreversible fibre fouling, a rapid rinsing of
158
the fibre in de-ionized water after extraction and prior to desorption was implemented. It
159
was observed that no significant loss of analyte occurred up to 50 s of rinsing, thus, it was
160
chosen for further experiments. Subsequently, grape samples were subjected to extraction
161
applying a 50 s rinsing prior to desorption. Overall, the obtained results demonstrate an
162
ineffectual improvement in the fibre lifetime. In agreement with De Jager et al.12, after 20
163
extraction/desorption cycles in grape matrix the PDMS/DVB fibre was blackened and a
164
substantial decrease in extraction efficiency was observed, resulting in very
165
irreproducible results. After 10 extractions, the extraction efficiency had decreased by 3
166
to 41% and by the 20th extraction, the efficiency had dropped by 83 to 89%. The same
167
experimental set up was repeated for PDMS fibre to evaluate the performance of PDMS
168
coating, since the ability of PDMS to withstand complex matrix without changes in its
169
sorptive properties has been subject to study.9 The results obtained for both sets of
170
experiments are shown in Figure 1. Responses were normalized taking first extractions as
171
100 %. The results for PDMS coating indicated that, after 20 extractions, the extraction
172
efficiency had dropped by 8 to 14 %. Indeed, PDMS coating offered improved
173
repeatability and robustness to direct immersion in complex matrix, despite its low
174
sensitivity towards the studied analytes. Therefore, at this point the question of sacrificing
175
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
177
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
181
single fibre). (A) PDMS/DVB 65 µm; (B) PDMS 100 µm. Normalization performed
182
taken extraction efficiency of first extraction for each analyte as 100 %. Extractions were
183
peformed for 30 min at 30 ºC, from 9 g grape pulp with triazole pesticides at a
184
concentration of 100 ng g-1.
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PDMS-modified coating preparation and characterization
186
It was necessary to optimize the coating method (spraying or dipping) and the overall
187
parameters such as addition of solvent, rate of pulling and aperture diameter. The
188
spraying method resulted in highly irregular coatings, thus, the work proceeded using
189
dip-coating. The optimized procedure is presented in the experimental section. The
190
optimized PDMS outer layer was obtained for two layers of PDMS which resulted in
191
optimum surface coverage of the original coating. The study showed that thinner coatings
192
(1 layer) did not ensure total surface coverage, resulting in a coating that still exhibited a
193
porous surface. In addition, thicker coatings (3 layers) resulted in non-uniform surface
194
coverage in terms of thickness throughout the coating length and also rendering weaker
195
physical stability due to excessive thickness that could lead to stripping of the coating
196
when withdrawn inside the fibre needle. Figure 2 shows the SEM images of the coatings
197
after being covered with a 10 nm layer of gold on its surface. The SEM image shows the
198
formation of a thin PDMS film on the surface of the PDMS/DVB fibre. The image
199
presents a uniform, non-porous, and smooth surface throughout the coating. The PDMS
200
outer layer thickness for the optimized coating was estimated to be approximately 25-30
201
µm.
202
In order to investigate the reproducibility of the optimized overcoating procedure, the
203
intra-fibre (n=4), as well as the inter-fibre reproducibility (three fibres, 3 replicates each)
204
in both water and grape pulp matrices were found to be very good as indicated by R.S.D.
205
values ranging from 0.1 to 11.4%. The results obtained are summarized in Supplementary
206
Information Table S2.
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Analytical Chemistry
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Figure 2.SEM image of the PDMS-modified coating (2 layers): Surface morphology and
209
estimation of coating thickness using 900x magnification.
210
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Triazoles Extraction
212
At first, DI-SPME of triazole compounds from water matrix was used to evaluate the
213
effect of the external PDMS layer on extraction capabilities of the PDMS/DVB coating
214
by comparing its extraction time profiles with those obtained with commercial
215
PDMS/DVB 65 µm fibre. Profiles of extraction obtained with the PDMS-modified fibre
216
shown in Figure 3 resulted very similarly for all the triazole pesticides studied. This is
217
compared to non-modified PDMS/DVB fibre, where only marginal differences could be
218
observed at shorter extraction times as a result of the additional step of diffusion of the
219
analytes through the PDMS outer layer. Such an effect is better illustrated in
220
Supplementary Information Figure S1, where it can be noted that the slopes of the initial
221
stage of the adsorption profiles for triazole pesticides were only slightly decreased for
222
PDMS overcoated fibre as compared to the non-modified fibre coating. However,
223
statistical analysis of both extraction time profiles by means of t-test indicates that the
224
kinetics of extraction was not influenced, by the additional barrier. Therefore, in the
225
studied matrix-analyte-coating system, the diffusion through the thin PDMS outer layer
226
does not statistically reduces the rate of mass transfer even at pre-equilibrium extraction
227
times. From a practical point of view, the obtained results are of utmost importance,
228
since most SPME applications are performed in pre-equilibrium conditions. In the present
229
work, the application of such modified coating in pre-equilibrium conditions does not
230
jeopardize the overall sensitivity towards triazoles that would be achieved by the
231
commercial PDMS/DVB coating. Additionally, as Figure 3 illustrates, the amount of
232
analyte extracted at equilibrium or near equilibrium by the PDMS-modified coating is
233
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
235
of the original PDMS/DVB coating by the additional PDMS layer, thus, no impairing of
236
extraction capabilities of the original coating. In the present study, it seems that the
237
PDMS layer does not substantially change either kinetic or thermodynamic parameters
238
associated with the original coating.
239
It is worth emphasize that in this new configuration, the analytes after crossing the
240
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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Analytical Chemistry
242
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
244
in some cases the kinetics of the extraction process (i.e. short extraction times
245
applications). The reduction in the rate of mass transfer is dependent on the thickness of
246
the overcoating, as well as on the differences in the distribution constant between the
247
overcoated polymer and the extraction polymer. Therefore, according to SPME
248
fundamentals, one might expect that different behaviors could be obtained for thicker
249
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
254
PDMS/DVB fibre and PDMS/DVB/PDMS fibre. (A) Full extraction time profile (up to
255
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
260
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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288
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
B
C
D
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304 305
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.
334 335 336
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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Analytical Chemistry
For TOC only
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