Technical Papers
Mar 25, 2015

UV Photodegradation of Enoxacin in Water: Kinetics and Degradation Pathways

Publication: Journal of Environmental Engineering
Volume 141, Issue 10

Abstract

Fluoroquinolones, such as enoxacin, are poorly removed by common sewage-treatment processes, leading to their discharge into the environment, where they have unknown, and potentially serious, impacts on plants and aquatic organisms. The aim of the research reported in this paper was to understand the degradation of enoxacin by direct UV (ultraviolet) photolysis and advanced oxidation processes (AOPs) involving UV/H2O2 and photo-Fenton [UV/H2O2/Fe(II)], which may provide an alternative method of removing this compound from water in a treatment plant. Aqueous samples of enoxacin (0.06 mM) were irradiated at 254 nm (Io=2×1016photons1). The presence of H2O2, as well as the addition of FeSO4·7H2O (photo-Fenton process) both resulted in faster degradation kinetics compared to direct irradiation, with all of these systems leading to significant mineralization of enoxacin [>80% removal of total organic carbon (TOC)] within 30 min. The kinetics for the degradation of enoxacin in the presence of natural organic matter (NOM) isolates were also evaluated. Analysis of reaction byproducts by liquid chromatography–mass spectrometry (LC–MS) suggested that photolysis of enoxacin results in hydroxylation, defluorination, and formation of a geminal diol. Proton nuclear magnetic resonance (H1-NMR; in D2O) was used for further verification. In addition, the rate constant for the hydroxyl radical (OH) reaction with enoxacin was determined by pulse radiolysis studies to be (5.91±0.08)×109Lmol1s1. These results suggest that OH may play an important role in the photoinduced removal of enoxacin from water, and these systems may be used to remove this compound in treatment plants.

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Acknowledgments

The U.S. National Science Foundation (NSF) and the Royal Society of New Zealand are thanked for their generous financial support in the form of an East Asia and Pacific Summer Institutes (EAPSI) scholarship to the first author. The sixth author received partial support from NSF Chemical, Bioengineering, Environmental, and Transport Systems (CBET)-1034555, and the Notre Dame Radiation Laboratory (U.S. DOE) provided the facilities to carry out the pulse radiolysis studies. Nicky McHugh is also thanked for assisting with TOC measurements at the Department of Zoology, University of Otago, Dunedin, New Zealand.

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Go to Journal of Environmental Engineering
Journal of Environmental Engineering
Volume 141Issue 10October 2015

History

Received: Nov 15, 2014
Accepted: Jan 21, 2015
Published online: Mar 25, 2015
Discussion open until: Aug 25, 2015
Published in print: Oct 1, 2015

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Hanoz Santoke [email protected]
Lecturer, Dept. of Chemistry, California State Univ., 9001 Stockdale Highway, Bakersfield, CA 93311; formerly, Urban Water Research Center, Dept. of Civil and Environmental Engineering, Univ. of California, Irvine, CA 92697-2175 (corresponding author). E-mail: [email protected]
Alfred Y. C. Tong
Dept. of Chemistry, Univ. of Otago, P.O. Box 56, Dunedin 9054, New Zealand; and New Zealand National School of Pharmacy, Univ. of Otago, P.O. Box 56, Dunedin 9054, New Zealand.
Stephen P. Mezyk
Professor, Dept. of Chemistry and Biochemistry, California State Univ., Long Beach, CA 90840.
Kimberly M. Johnston
Dept. of Chemistry and Biochemistry, California State Univ., Long Beach, CA 90840.
Rhiannon Braund
Associate Professor, New Zealand National School of Pharmacy, Univ. of Otago, P.O. Box 56, Dunedin 9054, New Zealand.
William J. Cooper
Professor, Dept. of Civil and Environmental Engineering; and Director, Urban Water Research Center, Univ. of California, Irvine, CA 92697-2175.
Barrie M. Peake
Associate Professor, Chemistry Dept., Univ. of Otago, P.O. Box 56, Dunedin 9054, New Zealand.

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