phytoestrogens and 4-nonylphenol

Some endocrine disrupting compounds such as phthalates and phenols act non-genomically by inhibiting the sulfotransferase (SULT 1E1 and SULT 1A1) isoforms which inactivate estrogens by sulfonation. A range of environmental phenolic contaminants and dietary flavonoids was tested for inhibition of the human SULT 1A1, 1E1 and 2A1 isoforms. In particular, the plasticisers 4-n-octyl- and 4-n-nonyl-phenol inhibit SULT 1E1 with IC(50) values of 0.16 microM vs. 10nM estradiol while the 2-substituted chlorophenols show similar values. Flavonoids are also SULT inhibitors; tricin is a competitive inhibitor of SULT 1E1 with a K(i) of 1.5+/-0.8 nM. In a small pilot study to determine whether ingestion of soy flavonoids would affect SULT1A1 activity in vivo as well as in vitro, sulfonation of daidzein was reduced in a group of women 'at risk' of breast cancer, as compared with controls, although the SULT 1A1*1/SULT 1A1*2 allele ratio was not different. Endocrine disrupting effects in man may be multifactorial when components from both the diet and the environment act at the same point in steroid metabolism.

Topics: Adolescent; Adult; Arylsulfotransferase; Diet; Endocrine Disruptors; Environmental Exposure; Female; Flavonoids; Humans; Inhibitory Concentration 50; Phenols; Phytoestrogens; Pilot Projects; Sulfotransferases; Xenobiotics

In Europe, endocrine disruptors (EDs) have been defined as substances foreign to the body that have deleterious effects on the individuals or their descendants, due to changes in endocrine function. In the United States, EDs have been described as exogenous agents that interfere with the production, release, transport, metabolism, binding, action or elimination of the natural ligands responsible for maintaining homeostasis and regulating body development. These two definitions are complementary, but both indicate that the effects induced by EDs probably involve mechanisms relating in some way to hormonal homeostasis and action. EDs are generally described as substances with anti-oestrogenic, oestrogenic, anti-androgenic or androgenic effects. More recently, other targets have been evidenced such as the thyroid and immune system. Many different EDs are present in the various compartments of the environment (air, water and land) and in foods (of plant and animal origin). They may originate from food packaging, combustion products, plant health treatments, detergents and the chemical industry in general. In addition to the potential effects of these compounds on adults, the sensitivity of embryos and fetuses to many of the xenobiotic compounds likely to cross the placenta has raised considerable concern and led to major research efforts. With the exception of the clearly established links between diethylstilbestrol, reproductive health abnormalities and cancers, very little is known for certain about the effects of EDs on human health. Given the lack of available data, current concerns about the possible involvement of EDs in the increase in the incidence of breast cancer, and possibly of endometriosis and early puberty in girls, remain hypothetical. Conversely, the deterioration in male reproductive health is at the heart of preoccupations and progress in analyses of the relationship between EDs and human health. This literature review aims to describe the current state of knowledge about endocrine disruption, focusing in particular on the problem of food contaminants.

Topics: Abnormalities, Drug-Induced; Animals; Benzhydryl Compounds; Diethylstilbestrol; Endocrine Disruptors; Endocrine System Diseases; Environmental Health; Environmental Pollutants; Female; Fetus; Food Contamination; Gonadal Dysgenesis; Homeostasis; Humans; Industrial Waste; Infertility, Male; Male; Mammary Neoplasms, Experimental; Neoplasms; Pesticide Residues; Phenols; Phthalic Acids; Phytoestrogens; Plastics; Pregnancy; Prenatal Exposure Delayed Effects; Rats

The natural female sex hormone estrogens binds once inside the cell to a protein receptor to form a 'ligand-hormone receptor complex'. The binding activates the hormone receptor, which triggers specific cellular processes. The activated hormone receptor then turns on specific genes, causing cellular changes that lead to responses typical of a ligand-hormone receptor complex. Estrogens (especially estradiol) bring out the feminine characteristics, control reproductive cycles and pregnancy, influence skin, bone, the cardiovascular system and immunity. Natural hormones are more potent than any of the known synthetic environmental estrogens (except drugs such as diethylstilbestrol [DES]). Estrogen production varies according to different factors (gender, age and reproductive cycles). Women produce more estrogen than men and the production is more abundant during fetal development than in the postmenopausal period. Most natural estrogens are short-lived, do not accumulate in tissue and are easily broken down in the liver. In contrast to natural estrogens, estrogenic drugs such as ethynylestradiol diethylstilbestrol (DES), synthetic environmental estrogens such as beta-hexachlorocyclohexane (beta-HCH), polychlorinated biphenyls (PCBs), o, p, p'DDT, 4-nonylphenol (NP) and phytoestrogens such as isoflavones or lignans, are more stable and remain in the body longer than natural estrogens. Because most of these compounds are lipophilic, they tend to accumulate within the fat and tissue of animals and humans. Thus, depending on the natural estrogen levels, environmental estrogens may have different influences (mimicking, blocking or cancelling out estrogen's effects) on estrogen activities.

Topics: Age Factors; Animals; Cell Division; DDT; Diethylstilbestrol; Environmental Pollutants; Estradiol; Estrogens; Estrogens, Non-Steroidal; Fabaceae; Hexachlorocyclohexane; Humans; Isoflavones; Lignans; Molecular Structure; Phenols; Phytoestrogens; Plant Preparations; Polychlorinated Biphenyls; Sex Factors

The androgen receptor (AR) plays a critical role in prostate cancer development and progression. This study aimed to use a computerized docking approach to examine the interactions between the human AR and phyto-oestrogens (genistein, daidzein, and flavone) and xeno-oestrogens (bisphenol A, 4-nonylphenol, dichlorodiphenyl trichloroethane [DDT], diethylstilbestrol [DES]). The predicted three-dimensional structure of AR and androgens was established using X-ray diffraction. The binding of four xeno-oestrogens and three phyto-oestrogens to AR was analysed. The steroids estradiol and dihydrotestosterone (DHT) were used as positive controls and thyroxine as negative control. All the ligands shared the same binding site except for thyroxine. The endogenous hormones DHT and 17beta-oestradiol showed the strongest binding with the lowest affinity energy (< -10 kcal mol(-1)). All three phyto-oestrogens and two xeno-oestrogens (bisphenol A and DES) showed strong binding to AR. The affinities of flavone, genistein, and daidzein were between -8.8 and -8.5 kcal mol(-1), while that of bisphenol A was -8.1 kcal mol(-1) and DES -8.3 kcal mol(-1). Another two xeno-oestrogens, 4-nonylphenol and DDT, although they fit within the binding domain of AR, showed weak affinity (-6.4 and -6.7 kcal mol(-1), respectively). The phyto-oestrogens genistein, daidzein and flavone, and the xeno-oestrogens bisphenol A and DES can be regarded as androgenic effectors. The xeno-oestrogens DDT and 4-nonylphenol bind only weakly to AR.

Topics: Benzhydryl Compounds; Computer Simulation; DDT; Diethylstilbestrol; Flavones; Genistein; Humans; Isoflavones; Ligands; Phenols; Phytoestrogens; Receptors, Androgen