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The assessment of chemical mixtures is a complex topic for toxicologists, regulators, and the public. In this article the linkage between the science of toxicology and the needs of governmental regulatory agencies in the United States is explored through an overview of environmental regulations enacted over the past century and a brief history of modern toxicology. One of the goals of this overview is to encourage both regulators and scientists to consider the benefits and limitations of this science–regulatory relationship as they tackle existing issues such as chemical mixtures. It is clear that a) over the past 100 years chemical regulation and toxicologic research, have in large part, shared a common emphasis on characterization and regulation of individual chemicals. But chemical mixtures have been, and continue to be, evaluated at hazardous waste sites around the United States. For this reason the current U.S. Environmental Protection Agency guidelines for chemical mixtures assessment are also reviewed. These guidelines highlight the current practice of mixtures assessment, which relies primarily on the existing single-chemical database. It is also clear that b) the science and assessment of chemical mixtures are moving forward through the combined efforts of regulatory agencies and scientists from a broad range of disciplines, including toxicology. Because toxicology is at this exciting crossroads, particular attention should be paid to the forces (e.g., public demands, regulatory needs, funding, academic interests) that both promote and limit the growth of this expanding discipline.

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In humans and rodents, exposure to antiandrogenic chemicals during sexual differentiation can produce malformations of the reproductive tract. Perinatal administration of 100 or 200 mg vinclozolin (V) kg-1 day-1 during sexual differentiation in rats induces female-like anogenital distance (AGD), retained nipples, cleft phallus with hypospadias, suprainguinal ectopic scrota/testes, a vaginal pouch, epididymal granulomas, and small to absent sex accessory glands in male offspring. Vinclozolin is metabolized to at least two active forms, M1 and M2, that display antiandrogenic activity by binding the androgen receptor (AR). Here, we present information on the reproductive effects of oral treatment with low dosage levels of V during sexual differentiation of the male rat. Vinclozolin was administered to the dam at 0, 3.125, 6.25, 12.5, 25, 50, or 100 mg kg-1 day-1 from gestational day 14 to postnatal day 3 (the period of fetal/neonatal testicular testosterone synthesis and sexual differentiation). At doses of 3.125 mg V kg-1 and above, AGD was significantly reduced in newborn male offspring and the incidence of areolas was increased. These effects were associated with permanent alterations in other androgen-dependent tissues. Ventral prostate weight in one year old male offspring was reduced in all treatment groups (significant at 6.25, 25, 50, and 100 mg kg-1 day-1), and permanent nipples were detected in males at 3.125 (1.4%), 6.25 (3.6%), 12.5 (3.9%), 25 (8.5%), 50 (91%), and 100 (100%) mg V kg-1 day-1. To date, permanent nipples have not been observed in a control male from any study in our laboratory. Vinclozolin treatment at 50 and 100 mg kg-1 day-1 induced reproductive tract malformations and reduced ejaculated sperm numbers and fertility. Even though all of the effects of V likely result from the same initial event (AR binding), the different endpoints displayed a wide variety of dose-response curves and ED50's. The dose-response data for several of the functional endpoints failed to display an obvious threshold. These data demonstrate that V produces subtle alterations in sexual differentiation of the external genitalia, ventral prostate, and nipple tissue in male rat offspring at dosage levels below the previously described no-observed-effect-level (NOEL). These effects occur at a dosage level an order of magnitude below that required to induce malformations and reduce fertility. Hence, multigenerational reproduction studies of antiandrogenic chemicals that were not conducted under the Environmental Protection Agency's new Harmonized Multigenerational Test Guidelines, which include endpoints sensitive to antiandrogens at low dosage levels, could yield a NOEL that is at least an order of magnitude too high.

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Vinclozolin is a well-characterized antiandrogenic fungicide. It produces adverse effects when administered during sexual differentiation, and it alters reproductive function in adult male rats by acting as an androgen-antagonist. Two active metabolites of vinclozolin, M1 and M2, compete with natural androgens for the rat and human androgen receptors (ARs), an effect that blocks androgen-induced gene expression in vivo and in vitro. In addition to their effects during perinatal life, androgens play a key role in pubertal maturation in young males. In this regard, the present study was designed to examine the effects of peripubertal oral administration of vinclozolin (0, 10, 30, or 100 mg kg-1 day-1) on morphological landmarks of puberty, hormone levels, and sex accessory gland development in male rats. In addition, as binding of the M1 and M2 to AR alter the subcellular distribution of AR by inhibiting AR-DNA binding, we examined the effects of vinclozolin on AR distribution in the target cells after in vivo treatment. We also examined serum levels of vinclozolin, M1, and M2 in the treated males so that these could be related to the effects on the reproductive tract and AR distribution. Vinclozolin treatment delayed pubertal maturation (at 30 and 100 mg kg-1 day-1) and retarded sex accessory gland and epididymal growth. Serum luteinizing hormone (LH; significant at all dosage levels) and testosterone and 5 alpha-androstane, 3 alpha, 17 beta-diol (at 100 mg kg-1 day-1) levels were increased. Testis size and sperm production, however, were unaffected. It was apparent that these effects were concurrent with subtle alterations in the subcellular distribution of AR. In control animals, most AR were in the high salt cell fraction, apparently bound to the natural ligand and DNA. Vinclozolin treatment reduced the amount of AR in the high salt (bound to DNA) fraction and it increased AR levels in the low salt (inactive, not bound to DNA) fraction. M1 and M2 were found in the serum of animals from the two highest dosage groups, but they were present at levels well below their K1 values. In summary, these results suggest that when the vinclozolin metabolites occupy a small percentage of AR in the cell, this prevents maximal AR-DNA binding and alters in vivo androgen-dependent gene expression and protein synthesis, which in turn results in obvious alterations of morphological development and serum hormone levels. It is noteworthy that similar exposures during prenatal life result in a high incidence of malformations in male rats.