Endocrine disruptor issues in Japan

Monitoring of environmental chemicals in Japan has revealed that several endocrine active chemicals are in river water, sediments, and wildlife as well as in the human umbilical cord. In 2001, risk assessments of tributyltin and nonylphenol have been conducted by the Ministry of the Environment, Japan. Risk assessments of di(2-ethylhexyl)phthalate and di-isononyl phthalate have also been performed by the Ministry of Health, Labour and Welfare using a toxicological point of view in 2001. In this review, an overview of recent progress in endocrine disruptor research in Japan will be provided.

Calmodulin is a selective modulator of estrogen receptors

In the search for differences between ERalpha and ERbeta, we analyzed the interaction of both receptors with calmodulin (CaM) and demonstrated that ERalpha but not ERbeta directly interacts with CaM. Using transiently transfected HeLa cells, we examined the effect of the CaM antagonist N-(6-aminohexyl)-5-chloro-naphthalene sulfonilamide hydrochloride (W7) on the transactivation properties of ERalpha and ERbeta in promoters containing either estrogen response elements or activator protein 1 elements. Transactivation by ERalpha was dose-dependently inhibited by W7, whereas that of ERbeta was not inhibited or even activated at low W7 concentrations. In agreement with these results, transactivation of an estrogen response element containing promoter in MCF-7 cells (which express a high ERalpha/ERbeta ratio) was also inhibited by W7. In contrast, transactivation in T47D cells (which express a low ERalpha/ERbeta ratio) was not affected by this CaM antagonist. The sensitivity of MCF-7 cells to W7 was abolished when cells were transfected with increasing amounts of ERbeta, indicating that the sensitivity to CaM antagonists of estrogen-responsive tissues correlates with a high ERalpha/ERbeta ratio. Finally, substitution of lysine residues 302 and 303 of ERalpha for glycine rendered a mutant ERalpha unable to interact with CaM whose transactivation activity became insensitive to W7. Our results indicate that CaM antagonists are selective modulators of ER able to inhibit ERalpha-mediated activity, whereas ERbeta actions were not affected or even potentiated by W7.

Polychlorinated biphenyls interfere with androgen-induced transcriptional activation and hormone binding

Polychlorinated biphenyls (PCBs) are ubiquitous highly persistent manufactured chemicals known to bioaccumulate in the food chain. Exposure to PCBs has been implicated in a wide range of human health effects, including altering normal endocrine processes and reproductive function. However, very little is understood regarding the specific mechanisms by which PCBs may exert their effects in biological systems. We have examined the ability of PCBs to interfere with transcriptional activation of the androgen receptor (AR) and glucocorticoid receptor (GR) in an in vitro transcription-based reporter assay system. Four Aroclor PCB mixtures were found to antagonize AR-mediated transcription in the presence of the natural AR ligand dihydrotestosterone (DHT). The antagonistic activity of Aroclor mixtures increased in the following order: 1260 < 1242 < 1254 < 1248. These Aroclor mixtures had no discernible effect on GR activity. Aroclor 1254 in the absence of DHT exhibited weak agonistic responses in a dose-dependent manner with AR. Within a series of individual congeners, congeners 42, 128, and 138 are shown to antagonize AR activity. These congeners all share a common core chlorine substitution pattern. Ligand-binding studies demonstrate that endocrine activities of PCB mixtures and congeners on AR are likely due to direct and specific binding to AR ligand-binding domain.

Endocrine disruption in sexual differentiation and puberty. What do pseudohermaphroditic polar bears have to do with the practice of pediatrics?

What do pseudohermaphroditic polar bears and girls with premature breast development have in common? Hormones. Sexual differentiation and the initiation of secondary sexual characteristics, such as breast growth, are both under the control of the sex hormones estrogen and androgen. Abnormal differentiation of the internal or external genitalia in bears and early onset of breast development in girls also may have a common element--exposure to environmental hormones.

Differential activation of wild-type and variant forms of estrogen receptor alpha by synthetic and natural estrogenic compounds using a promoter containing three estrogen-responsive elements

Structure-dependent estrogen receptor alpha (ER alpha) agonist and antagonist activities of synthetic and natural estrogenic compounds were investigated in human HepG2, MDA-MB-231 and U2 cancer cell lines. Compounds used in this study include 4'-hydroxytamoxifen, ICI 182,780, bisphenol-A (BPA), 2',4',6'-trichloro-4-biphenylol (3Cl-PCB-OH), 2',3',4',5'-tetrachloro-4-biphenylol (4Cl-PCB-OH), p-t-octylphenol, p-nonylphenol, naringenin, kepone, resveratrol, and 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE). Cells were transfected with a construct (pERE(3)) containing three tandem estrogen responsive elements (EREs) and either wild-type estrogen receptor alpha (ER-wt) or variants expressing activation function-1 (ER-AF1) or AF-2 (ER-AF2). The ER agonist activities of the synthetic mono and dihydroxy aromatic compounds are comparable in all three-cell lines, whereas the activities of naringenin, kepone and resveratrol are dependent on cell context and expression of wild-type or variant forms of ER alpha. In contrast, the ER antagonist activities for these compounds were highly complex and, with the exception of 3Cl-PCB-OH, all compounds inhibited E2-induced wild-type or variant ER action. Results of this in vitro study suggest that the estrogenic and antiestrogenic activity of structurally diverse synthetic and natural estrogenic compounds is complex, and this is consistent with published data that often give contradictory results for these compounds.

Multiple responses in gene expression in fish treated with estrogen

During the last decade there has been a significant body of research conducted on environmental estrogens. These include industrial, agricultural and pest-control chemicals that bind to the estrogen receptor and induce biological changes during development or reproduction. Most of these changes are probably due to modified gene expression, since estrogen receptors function at this level. We have mapped qualitative gene expression responses (by differential display reverse transcriptase polymerase chain reaction, DD) in adult male sheepshead minnows (Cyprinidon variegatus) receiving high dose injections (5 mg/kg), or constant flow-through aquatic exposures to environmentally relevant concentrations (100 ng/l) of estradiol-17beta, and found them nearly identical. We have observed both up-regulation and down-regulation of transcripts, which fit into known responses to estradiol. Among the genes up-regulated are vitellogenin and several vitelline envelope proteins indicating that genes for proteins involved in egg development and maturation are susceptible to environmental estrogen exposure. While physiological changes caused by estradiol treatment are not totally explained by changes at the mRNA level, those changes can nevertheless be used as fingerprints to characterize an in vivo estrogenic response.