Biodegradation of the iodinated X-ray contrast media diatrizoate and iopromide

被引:109
作者
Kalsch, W [1 ]
机构
[1] ECT Oekotoxikol GMBH, D-65439 Floersheim, Germany
关键词
contrast media; diatrizoate; iopromide; degradation; activated sludge; surface water;
D O I
10.1016/S0048-9697(98)00340-4
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The degradation of the iodinated contrast media diatrizoate and iopromide was investigated in laboratory tests. With regard to the expected behaviour of the contrast media in the environment, test systems with activated sludge, river water and river water plus sediment were established. In some of the experiments C-14-labelled contrast media were used to study degradation at low concentrations and to detect the transformation products. Degradation by as well as binding to aerobic-activated sludge of diatrizoate was poor, suggesting that this substance is hardly retained in sewage treatment plants. In systems with river water and sediment deacetylation of diatrizoate started after a lag period of 3 weeks and followed first order kinetics with rate constants of approximately 0.15 day(-1). Two metabolites were formed that were stable until day 200 of aerobic incubation. Finally, further transformation of the aerobic metabolites was observed under anoxic conditions. In activated sludge, approximately 85% of iopromide were transformed into two metabolites. Like the parent compound they were highly hydrophilic and less than 16% were bound to sludge solids. In water/sediment systems, disappearance of iopromide started spontaneously with a first order constant of 0.04 day(-1). One metabolite that was stable throughout the incubation period was formed with a delay of 20 days. In river water the concentration-dependent disappearance of iopromide was studied. The shortest half-life was 3.1 days at a concentration of 16.0 mu mol l(-1) and increased at concentrations below and above this value. The metabolites of iopromide were not identified, but partial deiodination of iopromide was shown. Mineralisation of the two contrast media or their metabolites to carbon dioxide was not observed. (C) 1999 Elsevier Science B.V. All rights reserved.
引用
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页码:143 / 153
页数:11
相关论文
共 27 条
[1]  
BASSL A, 1967, INT J PRAKT CHEM, V36, P265
[2]   BIOCHEMICAL TRANSFORMATIONS OF HERBICIDE-DERIVED ANILINES - REQUIREMENTS OF MOLECULAR CONFIGURATION [J].
BORDELEA.LM ;
BARTHA, R .
CANADIAN JOURNAL OF MICROBIOLOGY, 1972, 18 (12) :1873-&
[3]   ENRICHMENT AND CHARACTERIZATION OF A METHANOGENIC BACTERIUM FROM THE OXIC UPPER LAYER OF THE OCEAN [J].
CYNAR, FJ ;
YAYANOS, AA .
CURRENT MICROBIOLOGY, 1991, 23 (02) :89-96
[4]  
DUNN J, 1990, INVEST RADIOL, V25, P102
[5]  
ENGELSMATENA U, 1996, THESIS U HAMBURG HAR, P145
[6]   Contamination of hospital wastewater with hazardous compounds as defined by 7a WHG [J].
Gartiser, S ;
Brinker, L ;
Erbe, T ;
Kümmerer, K ;
Willmund, R .
ACTA HYDROCHIMICA ET HYDROBIOLOGICA, 1996, 24 (02) :90-97
[7]   A SENSITIVE COLOUR REACTION FOR THE PAPER CHROMATOGRAPHIC DETECTION OF IODIDE, IODINATED TYROSINES AND THYRONINES [J].
GMELIN, R ;
VIRTANEN, AI .
ACTA CHEMICA SCANDINAVICA, 1959, 13 (07) :1469-1470
[8]  
GOLDMAN P, 1971, DEGRADATION SYNTHETI, P147
[9]   MECHANISMS OF BACTERIAL-DEGRADATION AND TRANSFORMATION OF CHLORINATED MONOAROMATIC COMPOUNDS [J].
HAGGBLOM, M .
JOURNAL OF BASIC MICROBIOLOGY, 1990, 30 (02) :115-141
[10]   Anaerobic degradation of halogenated benzoic acids coupled to denitrification observed in a variety of sediment and soil samples [J].
Haggblom, MM ;
Rivera, MD ;
Young, LY .
FEMS MICROBIOLOGY LETTERS, 1996, 144 (2-3) :213-219