2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
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Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />
P64 OPTIMALIZATION OF SPME METhOD<br />
FOR SPICE CONTENTuAL SubSTANCES<br />
DETERMINATION<br />
MICHAELA STOUPALOVá, MILADA VáVROVá,<br />
HAnA PLESKAČOVá, LUDMILA MRAVCOVá and<br />
VLADIMíR VEČEREK<br />
University of Veterinary and Pharmaceutical Sciences Brno,<br />
Faculty of Veterinary Hygiene and Ecology<br />
Palackého 1–3, 612 42 Brno, Czech Republic<br />
stoupalovam@vfu.cz<br />
Introduction<br />
The SPME method can be used to extract analytes from<br />
different matrices. It has been employed in the isolation of<br />
analytes from the air, food, water, and other matrices 1 . The<br />
SPME method has a number of major advantages such as fast<br />
rate, high sensitivity and good accuracy; the detection limit<br />
regularly achieved for the above-mentioned matrices ranges<br />
in ng kg –1 . First published in 1989, the SPME method is now<br />
a well established extraction method whose application has<br />
been assessed and documented 2 .<br />
The analyses of organic, fragrant, and flavouring components<br />
as well as sample preparation are usually started<br />
with the concentration of an analyte. If one considers a time<br />
demand, the passive SPME sampling technique is the quickest,<br />
with sample preparation not exceeding 30 minutes 3 .<br />
The consistency of the results and the reliability of detection<br />
with SPME as well as repeatability and reproducibility<br />
are influenced by a number of factors, like polymer polarity<br />
and the thickness of a polymer layer (stationary phase) on<br />
the surface of a fibre, the sampling method, the pH, the ionic<br />
strength of a solution, sample temperature, agitation, etc.<br />
Experimental<br />
The objective of this paper was the optimization of solid<br />
phase microextraction (SPME) method, which is used for<br />
determination of the essential oils in spice. Analytes were<br />
analysed by GC/MS.<br />
S P M E<br />
The SPME method was investigated with different<br />
fibers (polydimethylsiloxane – 100 μm thickness and polydimethylksiloxayne-divinylbenzene<br />
– 65 μm), extraction time<br />
(1; 2; 5; 10; 15; 20; 30; 40 and 60 minutes), extraction temperature<br />
(30; 40 and 50 °C) and incubation of sample (0; 5;<br />
10; 15; 20 minutes).<br />
G C / M S<br />
The determination itself was performed using the<br />
GC 6890n (Agilent Technologies, USA) with a massspectrometric<br />
detector 5973n MSD (Agilent Technologies,<br />
USA); for separation HP-5MS capillary column was used<br />
(30 m × 0.25 mm × 0.25 μm). The injector temperature was<br />
270 °C, the ion source temperature was 230 °C and the<br />
Transfer Line temperature was 250 °C. The temperature<br />
s461<br />
programme was 45 °C for period of 2 minutes, 5 °C min –1<br />
to 200 °C, 200 °C for period of 2 minutes; the total analysis<br />
time was 35 minutes. The flow-rate of the carrier gas (He)<br />
was constant, 1 ml min –1 .<br />
Results<br />
The aim hereof was to optimise the SPME method for<br />
determination of the essential oils in spice. We monitored<br />
influence of the stationary phase on the sorption of monitored<br />
analytes. We carried out comparison of two PDMS fibres<br />
(100 μm) and PDMS-DVB (65 μm). The results obtained are<br />
stated in Fig. 1. From it follows that the PDMS-DVB fibre<br />
(65 μm) shows higher sorption effectivity for all the monitored<br />
pesticides.<br />
Fig. 1. Influence of the fibre type on response of detectors for<br />
the monitored analytes<br />
Also the influence of temperature on sorption of the target<br />
compounds was monitored. The following temperatures<br />
were tested: 30, 40 and 50 °C. Lower-molecular-weight terpenes<br />
were shown to have the best responses at a temperature<br />
of 30 °C while for the medium-molecular-weight terpenes<br />
(around 150 g mol –1 ), the effect of different temperature on<br />
the adsorption of analytes wasn’t so strong. Terpenes with the<br />
highest molecular weight (204 g mol –1 ) exhibited the highest<br />
response at a temperature of 50 °C. On the basis of the results<br />
and literature data, the sorption value at 30 °C was selected.<br />
Various sorption times were measured (1; 2; 5; 10; 15;<br />
20; 30; 40, and 60 minutes) at temperature of 30 °C. The time<br />
of 15 minutes seems to be suitable for both the sensitivity and<br />
a good repeatability.<br />
This study also investigated the effect of sample conditioning<br />
before analyte sorption. The conditions of analysis<br />
Fig. <strong>2.</strong> Influence of the incubation time on response of detectors<br />
for the monitored analytes