Occurrence and Environmental Behavior of the Chiral Pharmaceutical Drug Ibuprofen in Surface Waters and in Wastewater

Pharmaceutical compounds can reach detectable concentrations in rivers and lakes if production and use are sufficiently large and the compounds show some mobility and persistence in the aquatic environment. In this study, we report on the occurrence and on the enantiomer composition of the chiral ph...

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Veröffentlicht in:Environmental science & technology 1999-08, Vol.33 (15), p.2529-2535
Hauptverfasser: Buser, Hans-Rudolf, Poiger, Thomas, Müller, Markus D
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creator Buser, Hans-Rudolf
Poiger, Thomas
Müller, Markus D
description Pharmaceutical compounds can reach detectable concentrations in rivers and lakes if production and use are sufficiently large and the compounds show some mobility and persistence in the aquatic environment. In this study, we report on the occurrence and on the enantiomer composition of the chiral pharmaceutical drug ibuprofen (IB) in surface waters and in samples from wastewater treatment plants (WWTPs). Enantioselective gas chroma tography and detection by mass spectrometry/mass spectrometry was used for analysis. IB was present in influents of WWTPs at concentrations of up to 3 μg/L with a high enantiomeric excess of the pharmacologically active S enantiomer (S ≫ R), as from human urinary excretion. The principal human urinary metabolites of IB, hydroxy-IB and carboxy-IB, were observed in WWTP influents at even higher concentrations. In contrast to other pharmaceutical compounds such as clofibric acid and diclofenac, IB and its metabolites are then efficiently degraded (>95%) during treatment in WWTPs. Laboratory incubation experiments confirmed this rapid degradation. In rivers and lakes, IB was detected at concentrations of up to 8 ng/L, generally with some excess of the S enantiomer; the IB metabolites were not detected ( S) enantiomer composition as compared to that from human metabolism. Inefficient WWTPs and direct discharges of untreated wastewater from storm events, however, can still be a source for increased levels of IB in surface water.
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In rivers and lakes, IB was detected at concentrations of up to 8 ng/L, generally with some excess of the S enantiomer; the IB metabolites were not detected (&lt;1 ng/L). Incubation of lake water fortified with (rac)-IB indicated a faster dissipation of the S enantiomer, thus resulting eventually in residues with a reversed (R &gt; S) enantiomer composition as compared to that from human metabolism. 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Sci. Technol</addtitle><date>1999-08-01</date><risdate>1999</risdate><volume>33</volume><issue>15</issue><spage>2529</spage><epage>2535</epage><pages>2529-2535</pages><issn>0013-936X</issn><eissn>1520-5851</eissn><coden>ESTHAG</coden><abstract>Pharmaceutical compounds can reach detectable concentrations in rivers and lakes if production and use are sufficiently large and the compounds show some mobility and persistence in the aquatic environment. In this study, we report on the occurrence and on the enantiomer composition of the chiral pharmaceutical drug ibuprofen (IB) in surface waters and in samples from wastewater treatment plants (WWTPs). Enantioselective gas chroma tography and detection by mass spectrometry/mass spectrometry was used for analysis. IB was present in influents of WWTPs at concentrations of up to 3 μg/L with a high enantiomeric excess of the pharmacologically active S enantiomer (S ≫ R), as from human urinary excretion. The principal human urinary metabolites of IB, hydroxy-IB and carboxy-IB, were observed in WWTP influents at even higher concentrations. In contrast to other pharmaceutical compounds such as clofibric acid and diclofenac, IB and its metabolites are then efficiently degraded (&gt;95%) during treatment in WWTPs. Laboratory incubation experiments confirmed this rapid degradation. In rivers and lakes, IB was detected at concentrations of up to 8 ng/L, generally with some excess of the S enantiomer; the IB metabolites were not detected (&lt;1 ng/L). Incubation of lake water fortified with (rac)-IB indicated a faster dissipation of the S enantiomer, thus resulting eventually in residues with a reversed (R &gt; S) enantiomer composition as compared to that from human metabolism. Inefficient WWTPs and direct discharges of untreated wastewater from storm events, however, can still be a source for increased levels of IB in surface water.</abstract><cop>Washington, DC</cop><pub>American Chemical Society</pub><doi>10.1021/es981014w</doi><tpages>7</tpages></addata></record>
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ispartof Environmental science & technology, 1999-08, Vol.33 (15), p.2529-2535
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source American Chemical Society Journals
subjects Analgesics
Applied sciences
Chemistry
Contamination
Continental surface waters
Degradation
Earth sciences
Earth, ocean, space
Engineering and environment geology. Geothermics
Environmental impact
Exact sciences and technology
Gas chromatography
ibuprofen
Mass spectrometry
Metabolites
Natural water pollution
Nonsteroidal anti-inflammatory drugs
Pollution
Pollution, environment geology
Seawaters, estuaries
Surface waters
Waste materials
Wastewater
Wastewaters
Water
Water treatment and pollution
Water treatment plants
title Occurrence and Environmental Behavior of the Chiral Pharmaceutical Drug Ibuprofen in Surface Waters and in Wastewater
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