Removal of selected non-steroidal anti-inflammatory drugs (NSAIDs), gemfibrozil, carbamazepine, β-blockers, trimethoprim and triclosan in conventional wastewater treatment plants in five EU countries and their discharge to the aquatic environment

被引:196
作者
Paxéus, N
机构
[1] Gryaab, S-418 34 Göteborg, Karl IX:s väg
关键词
discharge to aquatic environment; human pharmaceuticals; NSAIDs; removal in WWTP; triclosan;
D O I
10.2166/wst.2004.0335
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The removal of commonly used pharmaceuticals (ibuprofen, naproxen, diclofenac, gemfibrozil, carbamazepine, atenolol, metoprolol and trimethoprim) and a biocide (triclosan) in operating wastewater treatment plants in five EU countries has been studied. Under normal operating conditions the acidic drugs and triclosan were partially removed with removal rates varying from ca. 20 to >95%. The highest removal rate was found for ibuprofen and triclosan (>90%) followed by naproxen (80%), gemfibrozil (55%) and diclofenac (39%). Ibuprofen undergoes an oxidative transformation to corresponding hydroxy- and carboxy-metabolites, which contributes to its high removal rate. Disturbances in the activated sludge process resulted in lower removal rates for all acidic drugs, mostly for diclofenac (<10% removed) but also for ibuprofen (<60% removed). The treatment of wastewaters by activated sludge usually did not result in any practical removal (<10%) of neutral carbamazepine or basic atenolol, metoprolol and trimethoprim. The removal rates of the investigated drugs and triclosan are discussed in terms of mechanisms responsible for their removal. Discharges of carbamazepine, diclofenac, gemfibrozil, naproxen, triclosan and trimethoprim from WWTPs to the aquatic environment, expressed as the average concentration in the effluent and the daily discharged quantity per person served by WWTPs were assessed.
引用
收藏
页码:253 / 260
页数:8
相关论文
共 21 条
[1]  
ADVEEF A, 2000, PHARM RES, V17, P85
[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]   The influence of the physicochemical characteristics and pharmacokinetic properties of selected NSAID's on their transdermal absorption [J].
Beetge, E ;
du Plessis, J ;
Müller, DG ;
Goosen, C ;
van Rensburg, FJ .
INTERNATIONAL JOURNAL OF PHARMACEUTICS, 2000, 193 (02) :261-264
[4]   Fate and effects of triclosan in activated sludge [J].
Federle, TW ;
Kaiser, SK ;
Nuck, BA .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 2002, 21 (07) :1330-1337
[5]   From municipal sewage to drinking water: fate and removal of pharmaceutical residues in the aquatic environment in urban areas [J].
Heberer, T ;
Reddersen, K ;
Mechlinski, A .
WATER SCIENCE AND TECHNOLOGY, 2002, 46 (03) :81-88
[6]   Occurrence of antibiotics in the aquatic environment [J].
Hirsch, R ;
Ternes, T ;
Haberer, K ;
Kratz, KL .
SCIENCE OF THE TOTAL ENVIRONMENT, 1999, 225 (1-2) :109-118
[7]   Determination of antibiotics in different water compartments via liquid chromatography electrospray tandem mass spectrometry [J].
Hirsch, R ;
Ternes, TA ;
Haberer, K ;
Mehlich, A ;
Ballwanz, F ;
Kratz, KL .
JOURNAL OF CHROMATOGRAPHY A, 1998, 815 (02) :213-223
[8]   Pharmaceutical profiling method for lipophilicity and integrity using liquid chromatography-mass spectrometry [J].
Kerns, EH ;
Di, L ;
Petusky, S ;
Kleintop, T ;
Huryn, D ;
McConnell, O ;
Carter, G .
JOURNAL OF CHROMATOGRAPHY B-ANALYTICAL TECHNOLOGIES IN THE BIOMEDICAL AND LIFE SCIENCES, 2003, 791 (1-2) :381-388
[9]  
KUMMERER, 2001, PHARM ENV SOURCES SO
[10]  
McAvoy DC, 2002, ENVIRON TOXICOL CHEM, V21, P1323, DOI 10.1897/1551-5028(2002)021<1323:MOTIWT>2.0.CO