On-line preconcentration of perfluorooctanoic acid and perfluorooctanesulfonic acid by nonaqueous capillary electrophoresis

Separation of major environmental pollutants as perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) by capillary electrophoresis is reported for the first time. It is not possible to resolve the solutes in an aqueous media. However, the use of methanol and acetonitrile as the backg...

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Published inElectrophoresis Vol. 33; no. 14; pp. 2159 - 2166
Main Authors Knob, Radim, Maier, Vítězslav, Petr, Jan, Ranc, Václav, Ševčík, Juraj
Format Journal Article
LanguageEnglish
Published Germany Blackwell Publishing Ltd 01.07.2012
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Summary:Separation of major environmental pollutants as perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) by capillary electrophoresis is reported for the first time. It is not possible to resolve the solutes in an aqueous media. However, the use of methanol and acetonitrile as the background electrolyte (BGE) solvents allowed their rapid separation in an uncoated capillary. A major effort was put into BGE optimization in respect to both separation efficiency and detection for further on‐line preconcentration. 5 mmol.L‑1 naphthalene‐1‐sulfonic acid and 10 mmol.L‑1 triethylamine dissolved in ACN/MeOH (50:50 v/v) provided best separation and detection conditions. Next, the large‐volume sample stacking and the field‐amplified sample injection were applied and compared. Large‐volume sample stacking improved limits of detection (LODs) with regard to the standard injection by 69 times for PFOA and 143 times for PFOS with LODs of 280 and 230 nmol.L‑1, respectively. Field‐amplified sample injection improved LODs 624 times for PFOAand 806 times for PFOS with LODs 31 and 40 nmol.L‑1, respectively. Both preconcentration methods showed repeatabilities of migration times less than 1.2% RSD intraday and 6.6% RSD interday. The method was applied on PFOA and PFOS analysis in a sample of river water treated with solid‐phase extraction, which further improved LOD toward 5.6 × 10‑10 mol.L‑1 for PFOS and 6.4 × 10‑10 mol.L‑1 for PFOA and allows the method to be used for river water contamination screening or decomposition studies.
Bibliography:Operational Program Research and Development for Innovations - ERDF - No. CZ.1.05/2.1.00/03.0058
Operational Program Education for Competitiveness - ESF - No. CZ.1.07/2.3.00/20.0018
istex:0DEBCFE88F55822AE544D82A011A4BC2BE1F2AB0
Ministry of Education of the Czech Republic - No. MSM 6198959216
ArticleID:ELPS4288
ark:/67375/WNG-G97LGJT6-Q
ObjectType-Article-1
SourceType-Scholarly Journals-1
ObjectType-Feature-2
content type line 23
ISSN:0173-0835
1522-2683
DOI:10.1002/elps.201100665