Metabolism and fate of xeno-oestrogens in man

被引:20
作者
Liehr, JG
Somasunderam, A
Roy, D
机构
[1] Univ Texas, Med Branch, Dept Pharmacol & Toxicol, Galveston, TX 77555 USA
[2] Univ Alabama Birmingham, Sch Publ Hlth, Dept Environm Hlth Sci, Birmingham, AL 35294 USA
关键词
D O I
10.1351/pac199870091747
中图分类号
O6 [化学];
学科分类号
0703 ;
摘要
A large variety of chemicals of either natural or synthetic origin possess oestrogen-like activity and are thus called xeno-oestrogens. Some of these chemicals such as the pesticide methoxychlor rc:quire metabolic activation for their oestrogenic activity, whereas other compounds may themselves be oestrogenic and may be deactivated by their metabolism. In this chapter, the metabolism of representative examples of environmental oestrogen-like chemicals has been discussed to illustrate common trends in the large structural variety of xeno-oestrogens. The compounds included are zearalenone, methoxychlor, bisphenol A, DDT, P-sitosterol, and genistein and have been selected based on availability of information, the potential of exposure of humans and wildlife to the compounds, their industrial or agricultural importance, and the importance of metabolism for their activation or deactivation. The oestrogenic activity of phenolic xeno-oestrogens, a large class of compounds of natural or synthetic origin or their metabolites, likely is based on the weak oestrogen receptor binding of phenol. These compounds are mainly metabolized by analogy to steroidal oestrogenic hormones, i.e., by aromatic ring hydroxylation (catechol formation), subsequent methylation of the catechol and further phase II metabolism by glucuronide and/or sulfate formation. In contrast, the chlorinated hydrocarbon pesticides, which are weakly oestrogenic, are mainly metabolized by dehalogenation at relatively low metabolic rates. Thus, these compounds may persist in the body, accumulate in fatty tissues and provide a chronic reservoir of oestrogenic chemicals.
引用
收藏
页码:1747 / 1758
页数:12
相关论文
共 34 条
[1]   LIGNAN AND ISOFLAVONOID CONJUGATES IN HUMAN URINE [J].
ADLERCREUTZ, H ;
VANDERWILDT, J ;
KINZEL, J ;
ATTALLA, H ;
WAHALA, K ;
MAKELA, T ;
HASE, T ;
FOTSIS, T .
JOURNAL OF STEROID BIOCHEMISTRY AND MOLECULAR BIOLOGY, 1995, 52 (01) :97-103
[2]   QUANTITATIVE-DETERMINATION OF LIGNANS AND ISOFLAVONOIDS IN PLASMA OF OMNIVOROUS AND VEGETARIAN WOMEN BY ISOTOPE-DILUTION GAS-CHROMATOGRAPHY MASS-SPECTROMETRY [J].
ADLERCREUTZ, H ;
FOTSIS, T ;
LAMPE, J ;
WAHALA, K ;
MAKELA, T ;
BRUNOW, G ;
HASE, T .
SCANDINAVIAN JOURNAL OF CLINICAL & LABORATORY INVESTIGATION, 1993, 53 :5-18
[3]   MICROBIAL TRANSFORMATION OF BETA-SITOSTEROL AND STIGMASTEROL INTO 26-OXYGENATED DERIVATIVES [J].
AMBRUS, G ;
ILKOY, E ;
JEKKEL, A ;
HORVATH, G ;
BOCSKEI, Z .
STEROIDS, 1995, 60 (09) :621-625
[4]   IN-VIVO DNA ADDUCT FORMATION BY BISPHENOL-A [J].
ATKINSON, A ;
ROY, D .
ENVIRONMENTAL AND MOLECULAR MUTAGENESIS, 1995, 26 (01) :60-66
[5]   IN-VITRO CONVERSION OF ENVIRONMENTAL ESTROGENIC CHEMICAL BISPHENOL-A TO DNA-BINDING METABOLITE(S) [J].
ATKINSON, A ;
ROY, D .
BIOCHEMICAL AND BIOPHYSICAL RESEARCH COMMUNICATIONS, 1995, 210 (02) :424-433
[6]  
BOBERG KM, 1990, J BIOL CHEM, V265, P7967
[7]   TRANSFORMATION OF ZEARALENONE AND ZEARALENOL BY RAT ERYTHROCYTES [J].
CHANG, WM ;
LIN, JK .
FOOD AND CHEMICAL TOXICOLOGY, 1984, 22 (11) :887-891
[8]  
DEHAL SS, 1994, DRUG METAB DISPOS, V22, P937
[9]   DDT and testicular cancer [J].
Ekbom, A ;
WicklundGlynn, A ;
Adami, HO .
LANCET, 1996, 347 (9000) :553-554
[10]   ZEARALENONE METABOLISM AND EXCRETION IN THE RAT - EFFECT OF DIFFERENT DOSES [J].
FITZPATRICK, DW ;
ARBUCKLE, LD ;
HASSEN, AM .
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART B-PESTICIDES FOOD CONTAMINANTS AND AGRICULTURAL WASTES, 1988, 23 (04) :343-354