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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 />

P56 STRATEGIES TO REDuCE DETECTION<br />

LIMITS IN ThE ANALySIS OF bROMINATED<br />

FLAME RETARDANTS IN <strong>ENVIRONMENTAL</strong><br />

SAMPLES<br />

MICHAELA náPRAVníKOVá, JAnA PULKRABOVá,<br />

PETRA HRáDKOVá, JAKUB SCHůREK, JAn<br />

POUSTKA and JAnA HAJŠLOVá<br />

Institute of Chemical Technology, Prague, Department of<br />

Food Chemistry and Analysis, Technická 3, 166 28 Prague 6,<br />

Czech Republic,<br />

michaela.napravnikova@vscht.cz<br />

Introduction<br />

Polybrominated diphenyl ethers (PBDEs) represent<br />

an important class of brominated flame retardants (BFRs)<br />

which are widely used in various consumer products such as<br />

electronic equipment, textiles and plastics 1 . These chemicals<br />

are highly persistent and bioaccumulative what leads to their<br />

ubiquitous occurrence in the environment 2 , both in abiotic<br />

and biotic matrices.<br />

Compared to major group of organohalogenated persistent<br />

organic pollutants (POPs) such as polychlorinated biphenyls<br />

(PCBs), the levels of PBDEs in respective environmental<br />

compartments are typically lower by one order of magnitude.<br />

On this account, low detection limits (LODs) are needed for<br />

their reliable control.<br />

Gas chromatography coupled to mass spectrometry<br />

(GC/MS) operated in either electron ionization mode (EI)<br />

or in negative chemical ionization (nCI) are commonly<br />

employed analytical procedures of determination these compounds<br />

3 . In nCI mode monitoring of abundant bromine ions<br />

(m/z 79 and 81) provides a more sensitive and selective option<br />

compared to EI. nowadays, comprehensive two-dimensional<br />

(orthogonal) gas chromatography coupled to time-of-flight<br />

mass spectrometry (GC × GC/TOFMS) has become another<br />

challenging alternative to analyze very complex PBDEs mixtures<br />

4 .<br />

In any case, achieving low LODs is also associated with<br />

the amount of sample introduced into GC system. The most<br />

commonly used GC injection technique for PBDEs is a splitless<br />

injection mode 3 , however, several studies were reported<br />

a possibility to employ a large-volume programmed-temperature<br />

vaporizer injection (PTV) in the determination of these<br />

compounds 5 .<br />

This paper presents the method performance characteristics<br />

obtained in several GC systems used for quantification<br />

of PBDEs.<br />

Experimental<br />

For our experiments a standard mixture of most common<br />

PBDE congeners (BDEs no. 28, 47, 49, 66, 85, 99, 100, 153,<br />

154 and 183) purchased from AccuStandard inc. (USA) was<br />

used. The real-life sample containing trace amount of PBDEs<br />

was a purified extract obtained from fish tissue by procedure<br />

s445<br />

described by Hajšlová et al. 6 . To assess LODs achievable<br />

under various GC conditions following set-up were tested:<br />

• PTV-GC/MS (EI),<br />

• PTV-GC/MS (nCI),<br />

• GC/TOFMS (EI),<br />

• PTV-GC/TOFMS (EI).<br />

P T V - G C / M S ( E I ) a n d P T V - G C / M S<br />

( n C I )<br />

GC/MS analyses were performed on an Agilent 6890n<br />

gas chromatograph coupled to a mass selective detector<br />

(Agilent 5975XL Inert MSD) equipped with quadrupole<br />

analyzer operated in nCI or EI mode using splitless or PTV<br />

injection. The GC conditions were as follows: a DB-XLB<br />

capillary column (15 m × 250 μm i.d. × 0.1 μm, J&W Scientific);<br />

a oven temperature program: from 105 °C (held for<br />

vent time) to 260 °C (held for 1 min) at 50 °C min −1 then to<br />

300 °C at 20 °C min –1 and held for 3 min; carrier gas: helium<br />

with constant flow 1.5 ml min −1 . The MS was operating in the<br />

selected ion monitoring (SIM) mode (monitored ions were<br />

m/z 79, 81, 159, 161 and m/z 406, 484, 564, 484, 562 for<br />

nCI and EI mode, respectively). The MS (nCI) parameters<br />

were as follows: reagent gas: methane; temperatures of MSD<br />

interface, ion source, and quadrupole: 280 °C, 150 °C, and<br />

150 °C, respectively. The temperatures of MSD interface,<br />

ion source and, quadrupole for MS (EI) system were 280 °C,<br />

230 °C and, 150 °C, respectively.<br />

Four parameters for PTV injection were tested: vent<br />

time (VT), vent flow (VF), injection volume (IV) and splitless<br />

period. Starting injection temperature was 50 °C (held<br />

4.6 min) and it was ramped to 350 °C at 500 °C min –1 .<br />

G C / T O F M S a n d P T V - G C / T O F M S<br />

The analyses were performed on a Pegasus 4D instrument<br />

(Leco, USA) consisting of an Agilent 6890n gas chromatograph<br />

equipped with splitless and/or PTV injector and<br />

a Leco Pegasus III high-speed time-of-flight mass spectrometer.<br />

The same, DB-XLB capillary column was used for<br />

determination of analytes. The GC conditions were similar<br />

to PTV–GC/MS system. The interface temperature was<br />

280 °C. The MS acquisition rate was 11 Hz, the mass range<br />

35–850 amu, the ion-source temperature 300 °C, and the detector<br />

potential –1875 V.<br />

Results<br />

In the first part of this study, the implementation and optimalization<br />

of a PTV injection coupled with GC/MS (EI and/<br />

or nCI mode) was realized. A solvent standard solution of<br />

above mentioned PBDE congeners was used for optimalization<br />

PTV injection conditions. Optimal parameters assessed<br />

by the comparison of a peak height of individual analytes<br />

were as follows:<br />

•<br />

•<br />

vent time: 90 s<br />

vent flow: 60 ml min –1

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