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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

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