Effects of dose, administration route, and/or vehicle on decabromodiphenyl ether concentrations in plasma of maternal, fetal, and neonatal rats and in milk of maternal rats.

The effects of route and vehicle on blood and milk levels of decabromodiphenyl ether (DecaBDE; CASRN 1163-19-5) were investigated in the rat to assist in the design and conduct of a developmental neurotoxicity study. Blood plasma and/or milk concentrations were determined in dams, fetuses, and/or nursing pups after repeated DecaBDE administration by gavage throughout gestation or gestation and lactation using corn oil (CO) or soyaphospholipon/Lutrol F 127-water (SPL) as the vehicle. The impact of vehicle on plasma levels was also investigated in pups derived from naive dams after a single postnatal dose. This study reports for the first time fetal and neonatal plasma concentrations concurrent with those of maternal plasma and/or milk. Higher concentrations of DecaBDE were achieved in plasma and in milk with CO than with SPL. Furthermore, pups derived from dams treated with only SPL were lower in body weight, compared with those from dams treated with either CO, CO and DecaBDE, or SPL and DecaBDE. The study further shows that exposure to DecaBDE is relatively consistent across the dose range of 100 to 1000 mg/(kg · day) when administered in CO.

Embryo-fetal developmental toxicity study design for pharmaceuticals.

Assessment of potential developmental and reproductive toxicity of human pharmaceuticals is currently guided by the International Conference on Harmonization (ICH) S5(R2) document (available at http://www.ich.org). The studies that assess developmental hazard are generally conducted in rodents and rabbits. Based on the authors' collective experience, adequate designs (including range-finding studies) and the presentation of data for these studies are described in detail. In addition, the suggested initiation and then total duration of these studies in relation to clinical studies that enroll women of childbearing potential are described. Optional parameters that may be included in the studies are discussed, as are study designs that combine assessments of fertility and developmental toxicity. New methods that may replace or enhance current procedures are outlined. The details described herein will assist all laboratories performing these studies, individuals who need to plan for the studies, and regulatory agencies that ultimately review these studies.

Juvenile animal toxicity study designs to support pediatric drug development.

The objective of juvenile animal toxicity studies of pharmaceuticals is to obtain safety data, including information on the potential for adverse effects on postnatal growth and development. Studies in juvenile animals may assist in identifying postnatal developmental toxicities or other adverse effects that are not adequately assessed in the routine toxicity evaluations and that cannot be safely or adequately measured in pediatric clinical trials. Unlike the traditional reproductive and developmental toxicology studies that have been discussed in the accompanying reports, the design requirements for toxicity studies in juvenile animals are not explicitly defined in regulatory guidance. However, studies in juvenile animals can be useful in providing safety information necessary to enable pediatric clinical trials in pediatric patients or when there are special concerns for toxicities that cannot be safely or adequately measured in clinical trials. These juvenile animal toxicity studies are designed on a case-by-case basis. General design considerations and examples of study designs for assessment of juvenile animal toxicity are discussed.

Effects of green tea catechin on embryo/fetal development in rats.

Evidence suggests that the health benefits associated with green tea consumption are related to tea catechins. The objective of this study was to evaluate potential maternal and fetal effects of standardized heat-sterilized green tea catechins (GTC-H). GTC-H was gavage administered to mated female rats from gestation day 6 through 17, at doses of 0, 200, 600, and 2000 mg/kg/day. There were no GTC-H-related deaths or macroscopic findings. During the entire gestation period in the high-dose (2000 mg/kg/day)-treated group and during days 6-9 and 6-18 in the 600 mg/kg/day group, mean body weight gain was lower. Mean feed consumption was lower during gestation days 6-9 in the 600 mg/kg/day group and during gestation days 6-9 and 9-12 in the 2000 mg/kg/day group. Compared to the control group, mean body weights in the 600 and 2000 mg/kg/day groups were up to 5.1% and 7.7% lower during gestation days 9-20. GTC-H administration did not affect mean gravid uterine weights or intrauterine growth and survival. There were no GTC-H-related fetal malformations or developmental variations. Based on the results of this study, the no-observed-adverse-effect level (NOAEL) for GTC-H was 200mg/kg/day for maternal toxicity, and 2000 mg/kg/day for embryo/fetal development.

Developmental toxicity and uterotrophic studies with di-2-ethylhexyl terephthalate.

BACKGROUND: These studies were conducted to evaluate the potential adverse effects of di-2-ethylhexyl terephthalate (DEHT) exposure on in utero development in mice and rats. In addition, a uterotrophic assay for estrogenic activity was conducted in sexually immature rats. METHODS: In the developmental toxicity studies, diet containing DEHT was fed to four groups of mated female Crl:CD(SD)IGS BR rats (25/group) from gestation day (GD) 0-20 or Crl:CD1(ICR) mice (25/group) from GD 0-18. Concentrations within the feed were 0, 0.3, 0.6, and 1.0% for the rats and 0, 0.1, 0.3, and 0.7% for the mice. Laparohysterectomies were carried out on the last day of exposure and the numbers of fetuses, early and late resorptions, total implantations, and corpora lutea were recorded. The fetuses were weighed, sexed, and examined for external, visceral and skeletal malformations, and developmental variations. The dose rate from dietary DEHT exposure was 0, 226, 458, and 747 mg/kg/day in the rats and 197, 592, and 1382 mg/kg/day in the mice for the control, low, mid, and high-exposure groups, respectively. RESULTS: DEHT exposure did not affect clinical observations. A slight reduction in body weight gain was noted in the high-dose level rat group; the remaining groups were unaffected. At necropsy, increased liver weights were noted in the high-dose rat group and the mid- and high-dose mouse groups. Mean numbers of implantation sites and viable fetuses, mean fetal weights, and mean litter proportions of preimplantation loss, early resorptions, late resorptions, and fetal sex ratios were unaffected by DEHT exposures. No test article-related malformations or variations were observed at any concentration level in the rat and mouse developmental toxicity studies. In the uterotrophic assay for estrogenic activity, sexually immature female rats received oral gavage doses 20, 200, or 2000 mg DEHT/kg bw/day from postnatal day (PND) 19-21. A slight reduction in rate of body weight gain was noted on the first day of dosing in the high dose group, but no other indications of toxicity were evident. DEHT exposure did not affect wet or blotted uterine weight parameters in any of these dose groups. The NOEL for developmental toxicity in rats was 747 mg/kg/day and 1382 mg/kg/day in mice. The NOEL for estrogenic activity was 2000 mg/kg/day. The NOEL for maternal toxicity was 458 mg/kg/day in rats and 197 mg/kg/day in mice. CONCLUSIONS: The lack of adverse developmental effects with DEHT exposure are in contrast to the adverse developmental effects noted after di-2-ethylhexyl phthalate (DEHP) exposure. The difference between the effects noted with the ortho-constituent (DEHP) and the lack of effects reported with the para-constituent (DEHT) is due most likely to differences in metabolism and the formation of the stable monoester, mono-2-ethylhexyl phthalate (MEHP) from the DEHP moiety.

Absence of embryo-fetal toxicity in rats or rabbits following oral dosing with nelfinavir.

The potential for nelfinavir mesylate (VIRACEPT) to induce maternal and embryo-fetal toxicity was evaluated in rats and rabbits following oral administration. The drug was administered by gavage to rats at doses of 200, 500, or 1000mg/kg/day on days 6-17 of gestation and to rabbits at doses of 200, 400, or 1000mg/kg/day on days 7-20 of gestation. Dams and does were euthanized on GD20 and 29, respectively, and the offspring were weighed and examined for external, visceral, and skeletal alterations. Maximum plasma nelfinavir concentrations (C(max)) in rats were comparable to C(max) values in humans and were 3- to 6-fold higher than the reported human trough levels, while plasma nelfinavir levels in rabbits were approximately 0.13-0.17x the human C(max) and 0.25-0.5x the human trough. In rats, no treatment-related maternal or embryo-fetal toxicity was observed at any dose level and the NOAEL for both maternal and fetal toxicity was considered to be 1000mg/kg/day. Two rabbits in the 400mg/kg/day group died prior to scheduled termination. Because no deaths occurred in the high dose group and there were no other treatment-related signs of clinical toxicity in any dose group, these deaths were considered unrelated to nelfinavir. Group mean body weight loss in rabbits was observed at 1000mg/kg/day on gestation days 7-10. Food consumption was also reduced in this treatment group throughout the dosing period. There were no treatment-related findings in other maternal or fetal parameters. Thus, the no-observed-adverse-effect-level (NOAEL) for maternal toxicity in the rabbit was considered to be 400mg/kg/day (based on maternal body weight loss in the high dose group), while the NOAEL for embryo-fetal toxicity in the rabbit was considered to be 1000mg/kg/day. Thus, under the conditions of this study, nelfinavir was not considered to be toxic to the rat or rabbit conceptus.

Absence of reproductive and developmental toxicity in rats following oral dosing with nelfinavir.

The potential for nelfinavir mesylate (VIRACEPT) to produce reproductive toxicity was evaluated in rats administered oral doses of 200, 500, or 1000mg/kg/day. In the fertility and early embryonic development to implantation study, male rats were treated beginning 28 days prior to mating until necropsy and females for 2 weeks prior to mating and through gestation day (GD) 7. In the pre- and postnatal development study, pregnant rats were treated from GD 6 through lactation day (LD) 20. Selected F(1) pups from this study were evaluated in sensory and behavioral tests and were subsequently mated. Pregnant F(1) females were euthanized on GD 20 and their F(2) fetuses were examined. F(1) animals were not directly dosed with the drug. No treatment-related effects were observed on any male reproductive parameters. Administration of nelfinavir did not produce adverse effects on fertility, pregnancy, embryo-fetal development, parturition, or lactation in the F(0) generation. Similarly, no adverse effects of nelfinavir treatment were observed on pre- and postnatal growth, development, reproductive performance and embryo-fetal development in the F(1) offspring. Based on the results of this study, the no-observed-adverse-effect-level (NOAEL) for developmental and reproductive toxicity in rats was considered to be 1000mg/kg/day, the highest dose tested.