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Developmental toxicity of inhaled N-methylformamide in the rat.

The developmental toxicity of N-methylformamide (MMF), an industrial chemical intermediate used in the production of agrichemicals, was examined in pregnant rats. MMF was administered by nose-only inhalation, 6 hr daily on Days 7-16 of gestation (the day copulation was confirmed was termed Day 1 of gestation, Day 1G) at exposure concentrations of 0, 15, 50, or 150 ppm. Dams were regularly monitored throughout gestation for body weight gain, feed consumption, and clinical signs. Cesarean sections were performed on Day 22G and the offspring were examined. Maternal toxicity was evident in dams exposed to 50 or 150 ppm; one dam exposed to 150 ppm died on Day 14G (considered to be treatment-related) and dams in the 50 and 150 ppm groups exhibited concentration-related clinical findings. Clinical signs of wheezing and rattling were observed both during and after the exposure period. The 150 ppm group also showed significant decreases in weight gain and feed consumption. A significant increase in the mean number of resorptions per litter at the 150 ppm level indicated an embryolethal effect. Developmental toxicity was apparent by a significant decrease in mean fetal body weight and increases in fetal malformations (subcutaneous cysts on the head, microphthalmia, anophthalmia, fused ribs and/or vertebra, and distended brain ventricles) and variations (misaligned and fused sternebrae) due to retarded development at 150 ppm. Significant fetal body weight decreases were also present at 50 ppm. Thus, in this study, the no-observable-adverse-effect level for both dam and fetus was 15 ppm MMF, indicating that for the parameters included in this study, the conceptus is not uniquely sensitive to MMF.

Administration, Inhalation↗

Atenolol developmental toxicity: animal-to-human comparisons.

BACKGROUND: Atenolol, 4-2'-hydroxy-3'-isopropyl-aminopropoxy) phenylacetamide, is a beta-adrenoreceptor blocker used for treatment of hypertension in pregnancy. Beta-blockers are reported to cause fetal harm (such as decreased birth weight) when administered to a pregnant woman. We evaluate published human and animal evidence of atenolol developmental toxicity and compare the manifestations in humans and in routinely-used animal models. METHODS: The comparison is based on the following criteria: comparability of pharmacokinetic/pharmacodynamic characteristics, type of adverse outcome, lowest adverse effect levels, and specificity and selectivity of effect. RESULTS: Manifestations of atenolol prenatal toxicity (placental changes, intrauterine growth retardation and changes in fetal weight in the absence of structural malformations) are similar in the tested animal species (rats and rabbits) and humans. The human seems to be more sensitive, however, because adverse embryo-fetal effects are reported at doses much lower than those in the tested species. In humans and rats, adverse embryo-fetal effects are induced by doses that are not maternally toxic. In the rabbit, however, such effects are seen only at maternally toxic doses, suggesting that in this species, developmental toxicity may be maternally mediated. CONCLUSIONS: The available data suggest animal-human concordance with regard to the nature and manifestations of atenolol prenatal toxicity. The animal models "predicted" developmental toxicity manifests as placental changes, intrauterine growth retardation and fetal weight decrease in the absence of structural malformations. Thus far, this is concordant with the data from humans, in whom intrauterine growth retardation has been observed but not structural abnormalities.

Abnormalities, Drug-Induced↗

Developmental toxicity study of pentachlorophenol in the rabbit.

The potential for developmental toxicity of pentachlorophenol (penta) was studied in New Zealand white rabbits at doses of 0 (corn oil), 7.5, 15, and 30 mg/kg/day administered by gavage on days 6 to 18 of gestation. The rabbits were sacrificed on day 29 of presumed gestation and necropsied. Measurements included number of corpora lutea, pregnancy, number and distribution of implantations, early and late resorptions, live and dead fetuses, fetal weight, gender, and gross external, soft tissue, and skeletal alterations. The mid and high doses reduced maternal body weight gain; the high dose caused transient weight loss and reduced feed consumption. There were no effects on embryofetal development at any of the doses evaluated. Based on these data, the maternal no-observable-adverse-effect level (NOAEL) is 7.5 mg/kg/day, while the developmental NOAEL is 30 mg/kg/day. Penta is not a developmental toxicant in a nonrodent animal model.

Animals↗

Developmental toxicity evaluation of butylparaben in Sprague-Dawley rats.

The developmental toxicity potential of butylparaben (CAS No. 94-26-8) was evaluated in rats. Sprague-Dawley rats were administered butylparaben in 0.5% carboxymethylcellulose by oral gavage at dose levels of 0, 10, 100, or 1,000 mg/kg/day on gestation days (GD) 6-19 (sperm positive day = GD 0). Caesarean sections were performed on GD 20 and fetuses were evaluated for viability, growth, and external, visceral, and skeletal abnormalities. Each group consisted of 25 females, with at least 21 per group being pregnant. The highest dose level caused decreases in maternal weight gain during some of the measurement intervals and was statistically significant during the GD 18-20 interval. Maternal food consumption was significantly decreased in the highest dose group over the dosing period (GD 6-20). There were no differences from control in any of the developmental parameters measured, including embryo/fetal viability, fetal weight, malformations, or variations. Based on the results of this study, the maternal NOAEL for butylparaben was 100 mg/kg/day. Butylparaben does not have the potential to cause developmental toxicity in the Sprague-Dawley rat at oral dosages up to 1000 mg/kg/day.

Abnormalities, Drug-Induced↗

Subchronic and developmental toxicity studies of n-butyl propionate vapor in rats.

Two inhalation studies were conducted to evaluate the possible subchronic and developmental toxic effects of n-butyl propionate. In the subchronic study, Sprague-Dawley rats (15/sex/group) were exposed to 0, 250, 750, or 1500 ppm vapor for 6 h/d, 5 d/wk for 13 wk. Five of the rats per sex per group were held after the final exposure for an 8-wk recovery period. Standard parameters of subchronic toxicity were measured throughout the study, and at the end of exposure and recovery periods, necropsies were performed, organs weighed, and tissues processed for microscopic examination. Exposure did not produce marked treatment-related deaths or adversely affect clinical signs, hematology, clinical chemistries, organ weights, or the histology of major visceral organs. The only systemic toxic effects were significant decreases in body weight, body weight gain, and feed consumption that occurred in 1500 ppm group rats. Morphologic changes were limited to the nasal cavity as evidenced by a concentration-related increased incidence and severity of olfactory epithelium degeneration in rats of the 750 and 1500 ppm groups. These degenerative microscopic alterations were primarily confined to the olfactory epithelium within the dorsal portion of the medial meatus, with lesser involvement of the olfactory mucosae overlying the tips of some of the adjacent ethmoturbinates. Both the systemic and nasal cavity effects appeared reversible after exposure ceased. In the developmental toxicity study, pregnant Sprague-Dawley rats (24/group) were exposed to 0, 500, 1000, or 2000 ppm vapor for 6 h/d on gestation d 6-15 and sacrificed on gestation d 20. All treatment-group dams exhibited significant reductions in body weight, body weight gain, and feed consumption. Gestational parameters were equivalent across all groups and there were no treatment-related developmental or teratogenic effects. The no-observed-adverse effects levels (NOAELs) determined for nbutyl propionate were 250 ppm for subchronic toxicity (based on the olfactory epithelium degeneration) and 22000 ppm for developmental toxicity (no developmental effects at top dose tested). Under the conditions of this study, a NOAEL was not determined for maternal toxicity.

Administration, Inhalation↗

Application of benchmark dose risk assessment methodology to developmental toxicity: an industrial view.

The U.S. EPA first signalled its intention to use benchmark dose risk techniques in 1991. Subsequently, publication of draft Guidelines for the Risk Assessment of Reproductive Toxicity data indicated the Agency's intention for wide use of the technique. In developmental toxicity experiments, a number of factors need to be considered before attempting benchmark dose calculations, as compared to the conventional NOAEL approach. For example, care in the assessment of potential litter effects (the litter is the unit of such a study) on the data and whether the data are continuous (e.g. foetal body weight) or discontinuous (e.g. specific or grouped developmental defects where the abnormality is present or absent). Two examples of the use of the benchmark dose approach will be made. First, in the analysis of foetal body weight, where a benchmark dose estimate for an agent producing a 5% decrease in mean foetal weight may be calculated from a shift in the distribution of foetal weights between groups, or by conversion of data to reflect changes in the incidence of 'small' pups (i.e. those towards the extreme of the normal range). The second example involves studies conducted on the developmental toxicity of a triazole antifungal. In the first study, the agent was clearly teratogenic, but a NOAEL was not established and thus necessitated a second study. Analysis of benchmark does estimates (e.g. for % foetuses malformed) from the first study indicated that these were not significantly changed when the data from the second study were combined (i.e. the second study did not aid the risk assessment). The benchmark dose approach has significant scientific and practical advantages over the conventional NOAEL methodology in risk assessments derived from developmental toxicity studies.

Animals↗

Relevance of the developmental toxicity of ethanol in the occupational setting: a review.

Numerous studies have been conducted investigating the reproductive toxicology of ethanol, the overwhelming majority concerning the adverse effects of consuming alcohol in beverages during pregnancy. Because many of the in vivo studies were designed to model alcoholism, they used comparatively high doses and assessed relatively few endpoints. Outcomes may have been affected by disturbances of metabolism at such high exposures, giving rise to secondary effects on development. The available data on ethanol from "conventional" developmental toxicity study test methods of the type used for regulatory hazard assessment of chemicals are limited. It is in this context, however, i.e. the use of ethanol as an industrial chemical rather than as a component of beverages, that this review is based. Using the usual criteria applied for the purpose of hazard assessment of industrial chemicals, it is concluded that there is no evidence that industrial exposure to ethanol is a developmental toxicity hazard. Developmental toxicity may result from drinking alcoholic beverages, the threshold level for all aspects of which has yet to be de fi ned. This is not, however, considered relevant to the low blood alcohol concentrations resulting from any conceivable inhalation or dermal exposure in the workplace or through the directed use of any consumer product containing ethanol.

Abnormalities, Drug-Induced↗

Evaluation of the maternal and developmental toxicity of aluminum from high doses of aluminum hydroxide in rats.

The potential of aluminum hydroxide [Al (OH)3] to induce developmental toxicity in rats was evaluated in the present study. Al (OH)3 was given by gavage at dose levels of 192, 384, and 768 mg/kg/day to groups of pregnant rats from day 6 through day 15 of gestation. Control animals received distilled water. Pregnant rats were evaluated for body weight, weight gain, food consumption, appearance, behavior and reproduction data. Cesarean sections were performed on gestation day 20, and the fetuses were removed for teratological evaluation. No significant maternal or developmental toxicity was observed at any Al (OH)3 dose level. Consequently, the no-observed-effect level (NOEL) for Al(OH)3 maternal or developmental toxicity would be greater than or equal to 768 mg/kg/day, which was the highest dose tested. This dose would be equivalent to a 60 kg person ingesting 16 g Al/day.

Aluminum Hydroxide↗

In vivo and in vitro structure-dosimetry-activity relationships of substituted phenols in developmental toxicity assays.

Structure-dosimetry-activity relationships (SDARs) of a series of substituted phenols were evaluated following exposure of gestation day 11 rats in vivo and in comparable stage embryos in vitro. In the in vivo study, 27 congeners were assayed and log P (a term used synomously with lipophilicity in this paper) and Hammett sigma values (a measure of the electronic withdrawing ability of the substituent) were shown to correlate with maternal toxicity; however, no relationships between these parameters and developmental effects were observed. In the in vitro system, 13 congeners were evaluated and molar refractivity and/or lipophilicity were shown to correlate with the ability of the phenols to induce embryonic growth retardation and structural defects in the absence of the hepatocytes. In contrast, when a metabolic activating system (primary hepatocytes) was present in the in vitro system, the potential to induce growth retardation was inversely related to lipophilicity, although the relationships were weaker than the positive relationship seen without the hepatocytes. The binding of the phenols to macromolecules in the culture medium was highly correlated with log P. Correcting the in vitro potency data for the variable amount of binding improved the predictiveness of the quantitative structure-activity relationships (QSARs). The potential to induce embryotoxicity in vitro was not well correlated with the potential to induce developmental toxicity in vivo: whereas the in vitro data demonstrates that the phenols are intrinsically embryotoxic, few of them actually produced significant developmental toxicity in the in vivo system, and there were few positive correlations between effects observed in the two systems.(ABSTRACT TRUNCATED AT 250 WORDS)

Abnormalities, Drug-Induced↗

Developmental toxicity evaluation of diethyl and dimethyl phthalate in rats.

Diethyl phthalate (DEP) and dimethyl phthalate (DMP), phthalic acid ester (PAE) plasticizers, were evaluated for developmental toxicity because of reports in the literature that some PAE were embryotoxic and teratogenic. A previous study (Singh et al., '72) suggested that an increased incidence of skeletal defects in rats might result from gestational exposure to DEP (0.6-1.9 g/kg) or DMP (0.4-1.3 g/kg), ip, on gestational days (gd) 5, 10, and 15. In the current study DEP (0, 0.25, 2.5, and 5%) or DMP (0, 0.25, 1, and 5%) in feed (approximately 0.2-4.0 g/kg/day) were supplied to timed-mated rats from gd 6 to 15. Treatment with 5% DMP resulted in increased relative maternal liver weight. Also, animals exhibited reduced body weight gain during treatment (5% DEP or DMP) and during gestation (5% DEP). Weight gain corrected for gravid uterine weight was also reduced in animals fed 5% DEP. However, high-dose treatment with either DEP or DMP resulted in changes in food and water consumption paralleling the body weight reductions, suggesting that apparent toxic effects on maternal body weight may reflect PAE/feed unpalatability. Treatment with 2.5% DEP resulted in only transient changes in body weight during early treatment. The only maternal effects at 0.25 or 1% DMP were minor changes in food and/or water consumption, and there were no effects at 0.25% DEP. Thus, the NOAELs for maternal toxicity were 1% DMP and 0.25% DEP. In contrast to the observed maternal toxicity, there was no effect of DEP or DMP treatment on any parameter of embryo/fetal development, except an increased incidence of supernumerary ribs (a variation) in the 5% DEP group. These results do not support the conclusion of other investigators that DEP and DMP are potent developmental toxicants. Rather, they suggest that the short-chain PAE are less developmentally toxic than PAE with more complex substitution groups, e.g., di(2-ethylhexyl) phthalate, mono(2-ethylhexyl) phthalate, and butyl benzyl phthalate.

Abnormalities, Drug-Induced↗

Potential human developmental toxicants and the role of animal testing in their identification and characterization.

Some 50 chemicals have been identified from environmental, occupational, or therapeutic exposure data as being potential developmental toxicants in humans. The toxicity pattern of these chemicals in humans has been characterized and correlated with developmental toxicity end points in laboratory animal models in order to determine the relevance and predictiveness of the results of testing in animals in extrapolation to human data. In general, animal developmental toxicity data closely paralleled human outcomes, and while humans in most cases were more sensitive than animals, the data support the concept that, imperfections aside, studies in animals serve a vital role in the hazard identification process.

Animals↗

Altered maternal zinc metabolism following exposure to diverse developmental toxicants.

It has been hypothesized that one mechanism contributing to the developmental toxicity of some xenobiotics is an embryonic/fetal zinc (Zn) deficiency that occurs secondary to toxicant-induced changes in maternal Zn metabolism. We studied the influence of diverse toxicants (urethane, ethanol, melphalan, arsenic, and alpha-hederin) on maternal-embryonic Zn metabolism and maternal liver metallothionein (MT) induction in Sprague-Dawley rats given a 65Zn-labelled meal by gavage 8 h after toxicant exposure and killed 10 h later on gestation day 12.5. Exposure to the toxicants resulted in increases in maternal hepatic MT concentrations that generally exceeded that which could be accounted for by reductions in food intake. 65Zinc retention was higher in maternal liver and lower in the products of conception in the toxicant-exposed groups. Strong linear relationships were found; as maternal liver MT concentrations increased, 65Zn retention in maternal liver was increased and 65Zn distribution to the conceptuses was decreased. These results support the hypothesis that diverse insults can produce developmental toxicity, in part, by altering maternal and embryonic Zn metabolism.

Animals↗

Developmental toxicity evaluation of the new fluoroquinolone antibacterial DW-116 in rats.

We have recently reported that the fluoroquinolone antibacterial DW-116 induces a significant developmental toxicity in rat. The present study was conducted to better understand the teratogenic effects of DW-116 at several developmental toxic doses in rats. DW-116 was orally administered to pregnant rats from gestational day (GD) 6 through 16 at dose levels of 0, 320, 400, and 500 mg/kg/day. All dams were subjected to caesarean section on GD 20 and their fetuses were examined for external, visceral, and skeletal abnormalities. At above 400 mg/kg, severe decreases in maternal body weight gain, food consumption, litter size, fetal weight and placental weight, and severe increases in resorption rate and fetal morphological alterations were observed. At 320 mg/kg, mild decreases in maternal body weight gain, food consumption, fetal weight and placental weight, and mild increases in fetal variations and retardations were observed. These results suggest that DW-116 is embryotoxic at above 320 mg/kg/day and is embryolethal and teratogenic at above 400 mg/kg in pregnant rats and that DW-116 is a selective developmental toxicant in rat conceptuses.

Abnormalities, Drug-Induced↗

Determination of a no-observed-effect level for developmental toxicity of ethylene glycol administered by gavage to CD rats and CD-1 mice.

Previous studies have indicated that ethylene glycol (EG) is a developmental toxicant in rats and mice primarily when ingested. This study was designed to establish no-observed-effect levels (NOELs) for developmental toxicity of EG administered by gavage in both rodent species. Dams were administered EG on Gestation Days 6-15; rats were given 0, 150, 500, 1000, or 2500 mg EG/kg/day; mice were dosed with 0, 50, 150, 500, or 1500 mg EG/kg/day. In rat dams given 2500 mg EG/kg/day, water consumption was increased during treatment and body weights were reduced throughout gestation; liver and kidney weights were increased at euthanization (Gestation Day 21). Relative liver weights were also increased at 1000 mg/kg/day. Effects observed in rat fetuses at 2500 mg/kg/day included the following: hydrocephaly; gastroschisis; umbilical hernia; fused, duplicated, or missing arches, centra, and ribs; poor ossification in thoracic and lumbar regions; and reduced body weights. Reduced body weights, duplicated or missing ribs, centra, and arches, and poor ossification were also observed in rat fetuses at 1000 mg/kg/day. In mice, there was no apparent treatment-related maternal toxicity. In mouse fetuses (Gestation Day 18), effects were observed at 1500 mg/kg/day and included reduced body weights, fused ribs and arches, poor ossification in thoracic and lumbar centra, and increased occurrence of an extra 14th rib. At 500 mg/kg/day, slight reductions in fetal body weight and increased incidences of extra ribs were observed. Under conditions of these studies, NOELs for developmental toxicity were 500 mg/kg/day for rats and 150 mg/kg/day for mice, indicating that mice were more susceptible than rats to the teratogenic effects of EG.

Abnormalities, Drug-Induced↗

Developmental toxicity evaluation of a scrubbing solution used in petroleum refineries.

The developmental toxicity potential of a scrubbing solution used extensively in petroleum refineries to remove CO2 from hydrogen gas streams was evaluated via inhalation. Pregnant female CD (Sprague-Dawley) rats were exposed to aerosols of a "used" scrubbing solution at 0.05, 0.1, 0.2, or 0.3 mg/l for 6 h/d on d 6-19 of pregnancy. Control animals were exposed to filtered air under the same exposure conditions. Dams were sacrificed on d 20 of pregnancy and a laparohysterectomy was performed. The mass median aerodynamic diameter of the aerosol revealed that all particles ranged from 1.6 to 2.8 microm, with geometric standard deviations between 2.0 and 2.3 microm. The overall pregnancy rate was high (>95%) and equivalent across all groups. All pregnant dams had live litters, and 22-24 litters were examined in each group. Treatment-related clinical signs consisted of rales, observed at all exposure levels, and gasping noted only at the 0.3 mg/l exposure level. The occurrence of rales was presumably a localized effect on the respiratory tract and likely due to the irritating properties of the scrubbing solution. Maternal toxicity was exhibited in the 0.3 mg/l group, including reduced body weight, weight gain, and food consumption and one possible treatment-related death on gestation d 17. At scheduled necropsy, there were no treatment-related gross pathological observations and no statistically significant reproductive and developmental effects. The incidences of fetuses with skeletal variations involving the sternum were clustered in two litters at the highest exposure level with atypically low term fetal body weights. Under the conditions of this investigation, potassium carbonate scrubbing solution is not a selective developmental toxicant.

Accidents, Occupational↗

A regression spline model for developmental toxicity data.

Observed dose-response patterns of data from several developmental toxicity experiments appear to be nonlinear and should be characterized by an appropriate model to adequately fit this observed pattern. Information from these animal studies of ambient substances that are noncarcinogenic, yet potentially toxic, to humans is used by federal protection agencies (Environmental Protection Agency, Occupational Safety and Health Administration, Food and Drug Administration) to determine safe exposure levels, such as no observed adverse effects level and benchmark dose. We have developed a flexible regression linear B-spline model for application to developmental toxicity dose-response data from animal studies of these noncarcinogens. We apply our model to data from two CD-1 mice studies of the National Toxicology Program; the observed dose-response pattern from both appears nonlinear: (1) experiment of 131 pregnant mice allocated over five exposure levels (0, 0.025, 0.05, 0.10, and 0.15% diet) of diethylhexyl phthalate and (2) experiment of 111 pregnant mice exposed to five levels (0, 62.5, 125, 250, and 500 mg/kg/day) of diethylene glycol dimethyl ether. In each study, we measure litter response as the proportion of adversely affected fetuses. Upon applying our B-spline model to the data from both studies, we predict nonlinear dose-response, with improvement over the more typical logistic dose-response model in each of the two studies.

Animals↗

Developmental toxicity of steviol, a metabolite of stevioside, in the hamster.

The developmental toxicity of steviol, a metabolite of stevioside, was studied in hamsters. Pregnant hamsters were intubated with steviol at dose levels of 0, 0.25, 0.5, 0.75 and 1.0 g/kg BW/day on days 6-10 of gestation. Steviol at doses of 0.75 and 1.0 g/kg BW/day were highly toxic to both dams and fetuses. Significant decrease of maternal body-weight gain during the experimental period (days 6-14) and high percentage of maternal mortality indicated the general toxicity of these two high doses. The number of live fetuses per litter and mean fetal weight also significantly decreased in the steviol-treated animals at doses of 0.75 and 1.0 g/kg BW day. The animals treated with an intermediate dose (0.50 g/kg BW/day) exhibited less signs of maternal and developmental toxicity than the two high doses (0.75 and 1.0 g/kg BW/day). One craniomeningocele was found in a fetus under the maternal toxic condition in steviol-treated at a dose of 0.75 g/kg BW/day. Neither the skeleton nor visceral development of the offspring was affected by steviol treatment except delayed ossification of the xiphoid (bifid) and long bones of the limbs and supernumerary thoracic ribs (14th ribs) tended to be increased at doses of 0.5 to 1.0 g/kg BW/day steviol. No dose-related teratogenesis was detected. From the result of the present study concerning maternal toxic condition and embryotoxicity, an oral dose of 0.25 g steviol/kg BW/day is regarded as having no observable effect. This steviol-treated dose is derived from stevioside 625 mg/kg BW/day which is approximately 80 times higher than the suggested acceptable daily intake of stevioside for humans (7.938 mg/kg BW/day).

Abnormalities, Drug-Induced↗

A study of the developmental toxicity potential of pentachlorophenol in the rat.

Pentachlorophenol (penta, CAS #87-86-5) is primarily used as a wood preservative. As part of the USEPA pesticide reregistration process, the developmental toxicity (embryo-fetal toxicity and teratogenic potential) of commercially available penta was studied following oral gavage to presumed pregnant female Sprague-Dawley rats (Crl:CD BR VAF/Plus Subdivision F, 83-3). Both study design and penta purity met the requirements of the USEPA. Doses of 0 (corn oil), 10, 30, and 80 mg/kg/day were administered to the rats at concentrations of 0, 2, 6, and 16 mg/ml, respectively from day 6 to day 15 of presumed gestation. The dosage volume was 5 ml/kg, adjusted on each day of dosage based on individual body weights recorded immediately before intubation. The rats were sacrificed on day 20 of presumed gestation and necropsied. The number of corpora lutea in each ovary was recorded. The uterus was examined for pregnancy, number and distribution of implantations, early and late resorptions and live and dead fetuses. Each fetus was weighed, sexed, and examined for gross external, soft tissue and skeletal alterations. The no-observable-adverse-effect-level (NOAEL) for maternal toxicity in rats was determined to be 30 mg/kg/day of penta. The developmental NOAEL for penta in rats was also found to be 30 mg/kg/day. The lowest-observable-adverse-effect-level (LOAEL) for penta developmental toxicity (80 mg/kg/day) was associated with increased resorptions, reduced live litter size and fetal body weights, and caused increased malformations and variations. These NOAELs, derived using USEPA approved study designs, are higher than those previously reported using penta that is no longer commercially available in studies with non-approved experimental designs. Penta should not be identified as a selective developmental toxicant in the rat because adverse effects on development of rat conceptuses occurred only at maternally toxic dosages.

Animals↗