Landfills and waste water treatment plants as sources of ... - GKSS
Landfills and waste water treatment plants as sources of ... - GKSS
Landfills and waste water treatment plants as sources of ... - GKSS
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METHOD OPTIMISATION<br />
Simonich et al. 2000; Bester 2004; Peck 2006). For determination <strong>of</strong> PBDEs the most<br />
frequently used injection systems are splitless <strong>and</strong> on-column injection (Covaci et al. 2003).<br />
Highly brominated PBDEs (octa- to decaBDE) are reported to be degraded during analytical<br />
process. Björklund et al. (2004) described the influence <strong>of</strong> GC settings on the determination<br />
<strong>of</strong> highly brominated PBDEs. If not selected properly, particularly column length <strong>and</strong><br />
injection technique may reduce the accuracy <strong>of</strong> the analytical method. Björklund et al. (2004)<br />
tested several inlets for the analysis <strong>of</strong> PBDEs. The authors concluded that the PTV inlet is<br />
the most suitable inlet for the analysis since the degradation <strong>of</strong> thermo-labile PBDEs is<br />
avoided.<br />
Due to the lack <strong>of</strong> functional groups which allows detection by other commonly applied<br />
detectors, all musk fragrances are routinely detected by m<strong>as</strong>s spectrometry (MS) (Yamagishi<br />
et al. 1981; Bester 2004; Peck et al. 2006; Lignell et al. 2008). Nitro musks have successfully<br />
been analysed with electron impact ionisation (EI) <strong>as</strong> the nitro groups give sufficient response<br />
(Rimkus 1999). In the EI mode <strong>of</strong> MS, usually three m<strong>as</strong>s fragments from the musk<br />
fragrances are produced <strong>as</strong> result <strong>of</strong> a cleavage between one or more methyl groups. So far,<br />
indications <strong>of</strong> co-elution <strong>of</strong> other substances within the m<strong>as</strong>s spectra were not observed<br />
(Bester 2009). However, musk fragrances <strong>of</strong>ten contain impurities (stereoisomers) which<br />
cannot be detected properly even if advanced technologies such <strong>as</strong> t<strong>and</strong>em MS or high<br />
resolution MS are applied (Bester 2009).<br />
Detection <strong>of</strong> PBDEs w<strong>as</strong> performed using MS either in the EI mode or the negative chemical<br />
ionisation mode (NCI) (Eljarrat 2003). M<strong>as</strong>s spectrometry in the EI mode produces a good<br />
selectivity through the formation <strong>of</strong> M + <strong>and</strong> the [M-2 Br] + which are used for identification<br />
<strong>and</strong> quantification. However, EI mode h<strong>as</strong> a low sensitivity for higher brominated congeners,<br />
such <strong>as</strong> penta-, octa-, <strong>and</strong> decaBDE <strong>and</strong> is therefore not routinely applied (Covaci et al. 2003).<br />
Benefit <strong>of</strong> the NCI mode is the enhanced sensitivity towards the Br - ions (m<strong>as</strong>s-to-chargeratio,<br />
m/z= 79, 81) <strong>and</strong> is therefore widely applied to detect PBDEs. However, the<br />
quantification with compound-specific m<strong>as</strong>s-labelled st<strong>and</strong>ards is not possible, since they<br />
exhibit the same m<strong>as</strong>s signal. In trace analysis it is strongly suggested to apply m<strong>as</strong>s-labelled<br />
st<strong>and</strong>ards for quantification. Furthermore, due to the low selectivity using two bromine ions,<br />
coelutions <strong>of</strong> other brominated compounds such <strong>as</strong> polybrominated biphenyls <strong>and</strong> MeO-<br />
PBDEs were reported (Stapleton 2006).<br />
For the quantification <strong>of</strong> musk fragrances only two m<strong>as</strong>s-labelled internal st<strong>and</strong>ards (IS) are<br />
commercially available. Those are the deuterated musk xylene (MX D15) <strong>and</strong> the deuterated<br />
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