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Landfills and waste water treatment plants as sources of ... - GKSS

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METHOD OPTIMISATION<br />

3.3 Extraction experiments<br />

3.2.5 Extraction method for PBDEs <strong>and</strong> musk fragrances <strong>of</strong> g<strong>as</strong>-ph<strong>as</strong>e samples<br />

Prior to the extraction experiments, precleaned PUF/XAD-2/PUF cartridges (n=3) were<br />

spiked with 50 μL <strong>of</strong> an internal st<strong>and</strong>ard solution containing m<strong>as</strong>s-labelled MBDE27,<br />

MBDE47, MBDE99, MBDE153, MBDE183 <strong>as</strong> well <strong>as</strong> both musk fragrances AHTN D3 <strong>and</strong><br />

MX D15 (c=200 pg μL -1 ). PUF/XAD-2/PUF cartridges were cold-column extracted in three<br />

cycles (1 h, 1 h, 30 min) using hexane/acetone 1:1 (v:v). After each cycle, solvent w<strong>as</strong> blown<br />

out with nitrogen. The volume <strong>of</strong> the solvent (approximately 450 mL) w<strong>as</strong> reduced using<br />

Synchore polyvap (Büchi, Essen, Germany) at a temperature <strong>of</strong> 45 °C <strong>and</strong> 415-380 mbar.<br />

Samples were further evaporated to 150 μL by a gentle stream <strong>of</strong> nitrogen. Finally, extracts<br />

were transferred to GC vials. Prior to the me<strong>as</strong>urements using GC-MS, 50 μL <strong>of</strong> an injection<br />

st<strong>and</strong>ard solution ( 13 C HCB <strong>and</strong> Fluoranthene D10, c=400 pg μL -1 ) w<strong>as</strong> added to the samples.<br />

For quantification a seven point calibration w<strong>as</strong> used (2, 4, 10, 20, 50, 80, 100, 200 pg μL -1 ).<br />

Linearity <strong>of</strong> calibration w<strong>as</strong> checked <strong>as</strong> described in DIN 32645 (1994). Peaks were<br />

quantitated b<strong>as</strong>ed on their peak are<strong>as</strong> <strong>and</strong> calculated using the internal st<strong>and</strong>ard method.<br />

3.2.6 Extraction method for PBDEs <strong>and</strong> musk fragrances <strong>of</strong> particle-ph<strong>as</strong>e samples<br />

Accelerated solvent extraction (ASE)<br />

GFF (n=3) were folded <strong>and</strong> filled into extraction cells (stainless steel, volume= 22 mL) <strong>of</strong> an<br />

accelerated solvent extractor (ASE, ASE 200, Dionex, Idstein, Germany). 50 μL <strong>of</strong> an internal<br />

st<strong>and</strong>ard solution containing m<strong>as</strong>s-labelled MBDE27, MBDE47, MBDE99, MBDE153,<br />

MBDE183 <strong>as</strong> well <strong>as</strong> both musk fragrances AHTN D3 <strong>and</strong> MX D15 (c=200 pg μL -1 ) w<strong>as</strong><br />

added. Remaining space in the cells w<strong>as</strong> filled up with precleaned diatomite (Fluka,<br />

Germany). Filters were extracted with hexane/acetone <strong>and</strong> pressurized to 140 bar at 100 °C.<br />

Two static cycles (5 min, hold time 5 min) were performed. After the first extraction cycle<br />

cell volume w<strong>as</strong> rinsed <strong>and</strong> refilled with solvent. The purge time w<strong>as</strong> set to 60 s. The volume<br />

<strong>of</strong> the extract (about 35 mL) w<strong>as</strong> reduced to 1 mL using Synchore polyvap. Extracts were<br />

further concentrated to 150 μL under a gentle stream <strong>of</strong> nitrogen. Prior to the me<strong>as</strong>urement<br />

using GC-MS, 50 μL <strong>of</strong> an injection st<strong>and</strong>ard solution containing 13 C HCB <strong>and</strong><br />

Fluoranthene D10 (c=400 pg μL -1 ) w<strong>as</strong> added to the samples. For quantification a seven point<br />

calibration w<strong>as</strong> used (2, 4, 10, 20, 50, 80, 100, 200 pg μL -1 ). Linearity <strong>of</strong> calibration w<strong>as</strong><br />

checked <strong>as</strong> described in DIN 32645 (1994). Peaks were quantitated b<strong>as</strong>ed on their peak are<strong>as</strong><br />

<strong>and</strong> calculated using the internal st<strong>and</strong>ard method.<br />

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