Photodegradation of common environmental pharmaceuticals and estrogens in river water

被引:244
作者
Lin, AYC [1 ]
Reinhard, M [1 ]
机构
[1] Stanford Univ, Dept Civil & Environm Engn, Stanford, CA 94305 USA
关键词
photolysis; photosensitization; pharmaceuticals; estrogens; surface water;
D O I
10.1897/04-236R.1
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Photodegradation rates of five pharmaceuticals (gemfibrozil, ibuprofen, ketoprofen, naproxen, and propranolol) and of four estrogens (estriol, estrone [E-1] 17 beta-estradiol [E-2], and 17 alpha-ethinylestradiol [EE2] which are common contaminants in the aquatic environment, were measured in both purified and river water at environmentally relevant concentrations (1-2 mu g/L) and different oxygen concentrations. Solutions were irradiated with a xenon arc lamp (765 W/m(2); 290 nm < lambda < 700 nm) and analyzed using a high-performance liquid chromatography-tandem mass spectrometry method with electrospray ionization for pharmaceuticals and atmospheric pressure photoionization for estrogens. In river water, half-lives were 4. 1 h for ketoprofen, 1. 1 min for propranolol, 1.4 h for naproxen, 2 to 3 h for estrogens, and 15 It for gemfibrozil and ibuprofen. In air-saturated purified water, rates generally were slower except for that of ketoprofen, which reacted with a half-life of 2.5 min. Naproxen, propranolol, and E, reacted with half-lives of 1.9, 4.4, and 4.7 h, respectively. The EE2, estriol, E-2, gemfibrozil, and ibuprofen reacted with half-lives of 28.4, 38.2, 41.7, 91.4, and 205 h, respectively. The presence of oxygen doubled the direct photolysis rates of naproxen and propranolol. In nonautoclaved river water, 80% of E-2 rapidly biotransformed to E-1 within less than 20 min, whereas all other compounds remained stable over 22 h.
引用
收藏
页码:1303 / 1309
页数:7
相关论文
共 33 条
[1]   Fate of estrogens in a municipal sewage treatment plant [J].
Andersen, H ;
Siegrist, H ;
Halling-Sorensen, B ;
Ternes, TA .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2003, 37 (18) :4021-4026
[2]   Pharmaceuticals in STP effluents and their solar photodegradation in aquatic environment [J].
Andreozzi, R ;
Marotta, R ;
Paxeus, N .
CHEMOSPHERE, 2003, 50 (10) :1319-1330
[3]   Monitoring natural and synthetic estrogens at activated sludge sewage treatment plants and in a receiving river water [J].
Baronti, C ;
Curini, R ;
D'Ascenzo, G ;
Di Corcia, A ;
Gentili, A ;
Samperi, R .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2000, 34 (24) :5059-5066
[4]  
Boscá F, 2001, PHOTOCHEM PHOTOBIOL, V74, P637, DOI 10.1562/0031-8655(2001)074<0637:POTNAI>2.0.CO
[5]  
2
[6]   Occurrence and environmental behavior of the chiral pharmaceutical drug ibuprofen in surface waters and in wastewater [J].
Buser, HR ;
Poiger, T ;
Muller, MD .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1999, 33 (15) :2529-2535
[7]   Occurrence and fate of the pharmaceutical drug diclofenac in surface waters: Rapid photodegradation in a lake [J].
Buser, HR ;
Poiger, T ;
Muller, MD .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1998, 32 (22) :3449-3456
[8]   Liquid chromatography-(tandem) mass spectrometry of selected emerging pollutants (steroid sex hormones, drugs and alkylphenolic surfactants) in the aquatic environment [J].
de Alda, MJL ;
Díaz-Cruz, S ;
Petrovic, M ;
Barceló, D .
JOURNAL OF CHROMATOGRAPHY A, 2003, 1000 (1-2) :503-526
[9]   DEVELOPMENT AND EVALUATION OF SUNLIGHT ACTINOMETERS [J].
DULIN, D ;
MILL, T .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1982, 16 (11) :815-820
[10]   Determination of drugs in surface water and wastewater samples by liquid chromatography-mass spectrometry:: methods and preliminary results including toxicity studies with Vibrio fischeri [J].
Farré, ML ;
Ferrer, I ;
Ginebreda, A ;
Figueras, M ;
Olivella, L ;
Tirapu, L ;
Vilanova, M ;
Barceló, D .
JOURNAL OF CHROMATOGRAPHY A, 2001, 938 (1-2) :187-197