ABSTRACT
It has been hypothesized that environmental contaminants that modulate endocrine signaling pathways may be causally linked to adverse health effects in humans. There has been particular concern regarding synthetic estrogens and their role in disrupting normal development of the male reproductive tract. Most estrogenic industrial compounds, such as bisphenol A (BPA) and nonylphenol, typically bind estrogen receptors alpha (ERalpha) and beta (ERbeta) and induce transactivation of estrogen-responsive genes/reporter genes, but their potencies are usually > or = 1,000-fold lower than observed for 17beta-estradiol (E2). Selective estrogen receptor modulators (SERMs) represent another class of synthetic estrogens that are being developed for treatment of hormone-dependent problems. The SERMs differentially activate wild-type ERalpha and variant forms expressing activation function 1 (ER-AF1) and AF2 (ER-AF2) in human HepG2 hepatoma cells transfected with a pC3-luciferase construct, and these in vitro differences reflect their unique in vivo biologies. The HepG2 cell assay has also been used in our laboratories to investigate the estrogenic activities of the following structurally diverse synthetic and phytoestrogens: 4'-hydroxytamoxifen; BPA; 2',4',6'-trichloro-4-biphenylol; 2',3',4',5'-tetrachloro-4-biphenylol; p-t-octylphenol; p-nonylphenol; naringenin; kepone; resveratrol; and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE). The results show that synthetic and phytoestrogens induce distinct patterns of gene activation in HepG2 and U2 osteogenic sarcoma cells, suggesting that these compounds will induce tissue-specific in vivo ER agonist or antagonist activities. The predicted differences between these compounds, based on results of the in vitro bioassay, have been confirmed. For example, BPA inhibits E2-induced responses in the rodent uterus, and HPTE and structurally related compounds are ERalpha agonists and ERbeta antagonists in assays carried out in HepG2 and other cancer cell lines.
Subject(s)
Environmental Exposure , Estrogens/toxicity , Isoflavones , Animals , Benzhydryl Compounds/toxicity , Diet , Estrogen Receptor Modulators/toxicity , Estrogen Receptor alpha , Estrogens, Non-Steroidal/pharmacology , Humans , Phytoestrogens , Plant Preparations , Receptors, Cell Surface/drug effects , Receptors, Cell Surface/metabolism , Receptors, Estrogen/drug effects , Receptors, Estrogen/metabolismABSTRACT
The rat, mouse and human estrogen receptor (ER) exists as two subtypes, ER alpha and ER beta, which differ in the C-terminal ligand-binding domain and in the N-terminal transactivation domain. In this study, we investigated the estrogenic activity of environmental chemicals and phytoestrogens in competition binding assays with ER alpha or ER beta protein, and in a transient gene expression assay using cells in which an acute estrogenic response is created by cotransfecting cultures with recombinant human ER alpha or ER beta complementary DNA (cDNA) in the presence of an estrogen-dependent reporter plasmid. Saturation ligand-binding analysis of human ER alpha and ER beta protein revealed a single binding component for [3H]-17beta-estradiol (E2) with high affinity [dissociation constant (Kd) = 0.05 - 0.1 nM]. All environmental estrogenic chemicals [polychlorinated hydroxybiphenyls, dichlorodiphenyltrichloroethane (DDT) and derivatives, alkylphenols, bisphenol A, methoxychlor and chlordecone] compete with E2 for binding to both ER subtypes with a similar preference and degree. In most instances the relative binding affinities (RBA) are at least 1000-fold lower than that of E2. Some phytoestrogens such as coumestrol, genistein, apigenin, naringenin, and kaempferol compete stronger with E2 for binding to ER beta than to ER alpha. Estrogenic chemicals, as for instance nonylphenol, bisphenol A, o, p'-DDT and 2',4',6'-trichloro-4-biphenylol stimulate the transcriptional activity of ER alpha and ER beta at concentrations of 100-1000 nM. Phytoestrogens, including genistein, coumestrol and zearalenone stimulate the transcriptional activity of both ER subtypes at concentrations of 1-10 nM. The ranking of the estrogenic potency of phytoestrogens for both ER subtypes in the transactivation assay is different; that is, E2 >> zearalenone = coumestrol > genistein > daidzein > apigenin = phloretin > biochanin A = kaempferol = naringenin > formononetin = ipriflavone = quercetin = chrysin for ER alpha and E2 >> genistein = coumestrol > zearalenone > daidzein > biochanin A = apigenin = kaempferol = naringenin > phloretin = quercetin = ipriflavone = formononetin = chrysin for ER beta. Antiestrogenic activity of the phytoestrogens could not be detected, except for zearalenone which is a full agonist for ER alpha and a mixed agonist-antagonist for ER beta. In summary, while the estrogenic potency of industrial-derived estrogenic chemicals is very limited, the estrogenic potency of phytoestrogens is significant, especially for ER beta, and they may trigger many of the biological responses that are evoked by the physiological estrogens.
Subject(s)
Environmental Pollutants/metabolism , Estrogens, Non-Steroidal/metabolism , Isoflavones , Receptors, Estrogen/metabolism , Binding, Competitive , Coumestrol/pharmacology , DDT/pharmacology , Estradiol/metabolism , Estrogens , Flavonoids/pharmacology , Humans , Phytoestrogens , Plant Preparations , Polychlorinated Biphenyls/pharmacology , Structure-Activity Relationship , Transcription, Genetic/drug effects , Zearalenone/pharmacologyABSTRACT
Large quantities of presumably nontoxic petroleum oil by-products are introduced into the environment as pesticide dispersal agents and emulsifiers. An increase in viral lethality with a concomitant influence on the liver and central nervous system occurs in young mice previously primed with such chemicals.