Effect of rodent diets on the sexual development of the rat.

Five rodent diets have been evaluated for their possible effect on the sexual development of the rat. Groups of 12 pregnant Alpk rats were fed one of the following combinations of diets during pregnancy and postnatally: RM3/RM1, AIN-76A/AIN-76A, RM3/AIN-76A, Teklad Global 2016 (Global)/Global and Purina 5001/Purina 5001. AIN-76A is phytoestrogen-free while the other diets contained varying amounts of phytoestrogens. The phytoestrogens genistein and daidzein were determined in the diets studied, and the concentrations found agreed with earlier estimates. RM3/RM1 was selected as the control group, as this has been used routinely in this laboratory for the past decade. Determinations were made in offspring of the times of vaginal opening and first estrus among the females, and of prepuce separation and testes descent among the males. At postnatal day (PND) 26 the females from 6 of the 12 litters were terminated and tissue weights measured. Males from 6 of the 12 litters were similarly studied at PND 68. Animals from the remaining litters were transferred to RM1 diet at PND 70. Termination of the study was at PND 128 (males) and PND 140 (females) when body weights and tissue weights were determined. Marked differences in body weight, sexual development, and reproductive tissue weights were observed for rats maintained on AIN-76A or Purina 5001, with only minimal effects among rats maintained on the Global diet. These comparisons were against RM3/RM1 as the reference diet. However, using Purina 5001 as the reference diet reversed the direction of the differences seen when using RM3/RM1 as the reference diet. The differences observed when using RM3/RM1 as reference diet occurred mainly postnatally. In addition, the fact that similar differences were seen for the phytoestrogen-free diet, AIN-76A, and the phytoestrogen-rich diet, Purina 5001, indicate that these effects are more likely to be caused by nutritional differences between the diets that then have centrally mediated effects on rodent sexual development, rather than individual dietary components affecting peripheral estrogen receptors (ER). This proposal is supported by abolition of the uterotrophic activity of AIN-76A and Purina 5001 (relative to RM3/RM1) in the immature rat by coadministration of the gonadotrophin-releasing hormone (GnRH) antagonist ANTARELIX: The present data indicate that choice of diet may influence the timing of sexual development in the rat, and consequently, that when evaluating the potential endocrine toxicity of chemicals, the components of rodent diets used should be known, and as far as is possible, controlled.

Subchronic toxicity (90-day) study with para-nonylphenol in rats.

As a component to the risk assessment process for para-nonylphenol (NP; CASRN 84852-15-3), a 90-day study was conducted in rats following U.S. EPA TSCA guidelines and Good Laboratory Practice regulations. NP was administered to four groups of rats at dietary concentrations of 0, 200, 650, or 2000 ppm which corresponded to approximate dietary intakes of 0, 15, 50, or 150 mg/kg/day, respectively. There were 25 rats/sex/group in the control and high-dose groups and 15 rats/sex/group in the low- and middose groups. Ten of the 25 rats/sex in the control and high-dose groups were designated as recovery animals and were maintained on control diets for 4 weeks after completion of the 90-day exposure period to assess the reversibility of any effects which might be observed. To evaluate for the possible weak estrogen-like activity that has been reported for NP in a number of screening assays, estrous cyclicity was monitored using vaginal cytology during Week 8 of the study, and sperm count, motility, and morphology were evaluated at termination. In-life effects from NP exposure were limited to small decreases in body weight and food consumption in the 2000-ppm dose group. Postmortem measurements at Week 14 indicated a dose-related kidney weight increase in males and a decrease in renal hyaline globules/droplets in males from the high-dose group. The kidney weights showed complete recovery following the 4-week postdosing recovery period. Due to the small magnitude of the changes (i.e., all weights were within or near laboratory historical control values) and the lack of correlating clinical or histopathological changes, the kidney weight alterations were not considered toxicologically significant. The biological significance of reduced hyaline in the kidneys of male rats from the high-dose group is uncertain. Renal tubular hyaline is associated with the rat-specific protein, alpha-2u-globulin, and, therefore, this finding was not considered toxicologically relevant to humans. No other effects attributable to NP were observed. No changes were observed for estrous cycling, sperm evaluations, or effects on endocrine organs. NP, therefore, did not manifest any estrogen-like activity as measured in these parameters at dietary concentrations as high as 2000 ppm, the maximum dose administered in this study. Based on the minor findings for the 2000-ppm dose group, the NOAEL (no-observed-adverse-effect level) for NP in this study is considered to be 650 ppm in the diet, corresponding to an approximate intake of 50 mg/kg/day.