
<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/">
  <dc:date>2024</dc:date>
  <dc:date>info:eu-repo/date/embargoEnd/2026-10-01</dc:date>
  <dc:format>application/pdf</dc:format>
  <dc:format>4730448 bytes</dc:format>
  <dc:type>info:eu-repo/semantics/article</dc:type>
  <dc:description xml:lang="eng">This paper presents the method for monitoring 7 PCB congeners (PCB 28, 52, 101, 118, 138, 153, and 180) from the US EPA priority, which can also be applied for quantification of PCB sums (28+31). The separation of the PCB 28 and PCB 31 was also examined. The GC-MS technique with the HP-5MS column and the accelerated solvent extraction (ASE) were applied. The accuracy and precision of the method were assessed as the recovery (R, %) of the spiked matrices and the relative standard deviation (RSD, %). The obtained recoveries for 17 spiked soil matrices (at the concentration level of 0.05 mg/kg) ranged from 73.8 % to 100.6 % and for spiked sediments from 80.2 % to 106.5 %. The RSD values ranged between 9.7 % and 15 % for soil and from 23 % to 33 % for sediment. The calculation of R and RSD were performed both for individual peaks as well as the sum of PCB (28+31). The recoveries of the certified reference materials (CRM) for soil and sediment were also calculated. The river sediment CRM recovery was in the range from 23.3 % (PCB 28+31) to 60 % (PCB 118) while recovery for soil CRM varied between 51.6 % for PCB (28+31) to 100.6 % for PCB 101. The z-score of the soil and sediment CRMs were in the satisfactory range ±2 for most PCB congeners. It was not possible to separate PCB 28 and PCB 31 for CRM soil.</dc:description>
  <dc:rights>info:eu-repo/semantics/embargoedAccess</dc:rights>
  <dc:rights>All rights reserved</dc:rights>
  <dc:source>Microchemical Journal</dc:source>
  <dc:source>volume: 207</dc:source>
  <dc:source>number: 111761</dc:source>
  <dc:source>startpage: 1</dc:source>
  <dc:source>endpage: 9</dc:source>
  <dc:identifier>https://unilib.phaidrabg.rs/o:5697</dc:identifier>
  <dc:identifier>doi:10.1016/j.microc.2024.111761</dc:identifier>
  <dc:identifier>ISSN: 0026-265X</dc:identifier>
  <dc:subject xml:lang="eng">PCB 28, PCB 31, soil, sediment, ASE</dc:subject>
  <dc:creator id="https://orcid.org/0000-0002-0053-4585">Nenin, Tanja</dc:creator>
  <dc:creator id="https://orcid.org/0009-0006-0162-6920">Petković, Anđelka</dc:creator>
  <dc:creator id="https://orcid.org/0000-0002-5991-1445">Mitrović, Tatjana</dc:creator>
  <dc:creator id="https://orcid.org/0000-0002-4407-1885">Čolić, Jasna</dc:creator>
  <dc:publisher>Elsevier Ltd., Amsterdam, Netherlands</dc:publisher>
  <dc:language>eng</dc:language>
  <dc:title xml:lang="eng">Validation of the GCMS    method for the determination of polychlorinated biphenyls congeners in soil and sediment samples</dc:title>
</oai_dc:dc>
