Richard E. Morrissey

The Developmental Toxicity of Bisphenol A in Rats and Mice

Bisphenol A (BPA) was evaluated for developmental toxicity in CD rats (0, 160, 320, or 640 mg/kg/day) and CD-1 mice (0, 500, 750, 1000, or 1250 mg/kg/day) dosed daily by gastric intubation on Gestational Days 6 through 15. Timed-pregnant dams were sacrificed 1 day prior to parturition, the uterine contents were examined, and all fetuses were examined for external, visceral, and skeletal malformations. In rats, maternal weight gain during gestation, weight gain corrected for gravid uterine weight, and weight gain during treatment were significantly reduced at all BPA doses. Gravid uterine weight and average fetal body weight per litter were not affected by BPA. No increase in percentage resorptions per litter or percentage fetuses malformed per litter was detected. In mice, maternal mortality occurred at all BPA doses, reaching 18% at the high dose, which also produced a significant decrease in maternal body weight gain during gestation and treatment. Weight gain corrected for gravid uterine weight was not affected by BPA. Reductions in gravid uterine weight and average fetal body weight were observed with the 1250 mg/kg dose of BPA. Relative maternal liver weight was increased at all doses of BPA. There was a significant increase in the percentage of resorptions per litter with 1250 mg BPA/kg/day. Malformation incidence was not altered by BPA. Thus, BPA treatment at maternally toxic dose levels during organogenesis produced fetal toxicity in mice but not in rats and did not alter fetal morphologic development in either species.

Results and Evaluations of 48 Continuous Breeding Reproduction Studies Conducted in Mice

Results of 48 continuous breeding reproduction (RACB) studies are summarized and control data from these studies are used to determine the statistical sensitivity of each endpoint from different parts of these studies. Results of testing individual chemicals compared well with results of multigeneration studies reported in the literature. Continuous breeding studies were able to discriminate reproductive toxicants from nontoxicants, and provided valuable structure-activity information. When mice in continuous cohabitation produce multiple litters, the statistical sensitivity of fertility endpoints is quite high and is comparable to that associated with other sensitive indicators of reproductive function, such as testis weight and sperm parameter measures. The principal advantages of the RACB protocol in comparison to multigeneration studies are: (1) the increased sensitivity and statistical power, (2) the ability to monitor progression of toxicity and to detect subfertility, (3) use of a battery of endpoints including sperm measures, (4) the ability to determine the affected sex(es), and (5) slightly reduced testing time.

Developmental Toxicity of Boric Acid in Mice and Rats

Boric acid (BORA), an ingredient of many cosmetics, pharmaceuticals, and pesticides, was tested for developmental toxicity in timed-pregnant Swiss mice and Sprague-Dawley rats (n = 26-28/group). BORA (0, 0.1, 0.2, or 0.4% in feed) was provided throughout gestation to attain steady-state exposure as early as possible during prenatal development. Average doses (mg/kg/day) were 248, 452, or 1003 in mice, and 78, 163, or 330 in rats. To limit prenatal mortality, BORA (0.8% or 539 mg/kg/day) was provided to an additional group of rats on Gestational Days (GD) 6 to 15 only. On GD 17 (mice) or 20 (rats), fetuses were weighed and examined for malformations (external, visceral, skeletal). Mouse dams exhibited mild renal lesions (greater than or equal to 0.1%), increased water intake and relative kidney weight (0.4%), and decreased weight gain (0.4%) during treatment. There was a reduction of fetal body weight (greater than or equal to 0.2%) and an increased incidence of resorptions and malformed fetuses per litter (0.4%). Morphological changes included an increased incidence of short rib XIII (a malformation) and a decreased incidence of rudimentary or full rib(s) at lumbar I (an anatomical variation). Maternal rats exhibited increased liver and kidney weights at greater than or equal to 0.2%, altered water and/or food intake at greater than 0.2%, and decreased weight gain at greater than 0.4%. Average fetal body weight/litter was reduced at all doses. Prenatal mortality was increased only at 0.8%. The incidence of fetal malformations was significantly increased at greater than or equal to 0.2%. The most frequently observed malformations were enlarged lateral ventricles of the brain and agenesis or shortening of rib XIII. In rats, the no-observable-adverse-effect level (NOAEL) for maternal toxicity was 78 mg/kg (0.1%), while in mice the low dose of 248 mg/kg (0.1%) approached the maternal NOAEL with mild renal lesions in only 2 of 10 females. Embryo/fetal toxicity occurred in all groups of rats at greater than or equal to 78 mg/kg (greater than or equal to 0.1%) while the NOAEL for developmental toxicity in mice was 248 mg/kg (0.1%). Thus developmental toxicity occurred below maternally toxic levels in rats as well as in the presence of maternal toxicity in mice and rats.

Evaluation of Rodent Sperm, Vaginal Cytology, and Reproductive Organ Weight Data from National Toxicology Program 13-Week Studies

Sperm morphology and vaginal cytology examinations (SMVCEs), which include evaluations of motility, concentration and head morphology of sperm from the cauda epididymis, and male reproductive organ weight data, were developed by the National Toxicology Program as a screening system for reproductive toxicants. An analysis was conducted of SMVCE studies carried out at the end of fifty 13-week studies (25 for rats, 25 for mice) over a 3-year period. Statistically significant changes in these studies were summarized, as were control data for each male endpoint (mean, SD, 95% confidence limits around the mean, median, and statistical power). Reproductive organ weights (testis, epididymis, cauda epididymis) and sperm motility were the most statistically powerful endpoints evaluated; sperm head morphology may also be a sensitive endpoint for detecting reproductive toxicants. For 24 chemicals tested in both rats and mice, the concordance of results [i.e., no adverse effect in either species, or at least one SMVCE endpoint (not necessarily the same one) adversely affected in both species] was 58%. These data suggest that detection of potential reproductive toxicants might be best when both species are used. Types of sperm head abnormalities and their relative proportion of the total did not differ among control and treatment groups. Estrous cycle data were obtained in the final week of forty-six 13-week studies (23 for mice, 23 for rats). Only 3 chemicals caused an increase in mean cycle length compared with the control group. More data from breeding studies in which female estrous cycle length is measured are needed to assess fully the association of cycle length with reproductive outcome; stages of the estrous cycle are so variable that they may not be useful in assessing potential toxicity. Interlaboratory variability in SMVCE values for many endpoints was documented. Very few of the chemicals that form the basis of this report have been evaluated in definitive reproductive toxicology protocols; a companion paper compares changes in SMVCE endpoints with the outcome of continuous breeding reproduction studies.

Retinoic acid and 2,3,7,8-tetrachlorodibenzo-p-dioxin selectively enhance teratogenesis in C57BL/6N mice☆

TCDD is one of the most toxic man-made compounds and an extremely potent teratogen in mice. Many of its toxic symptoms resemble those seen during vitamin A deficiency. Vitamin A and its derivatives, such as alltrans-retinoic acid (RA), are also teratogenic in mice, as well as many other species. Both TCDD and RA produce cleft palate in susceptible strains of mice. However, while TCDD produces hydronephrosis, RA does not, and TCDD does not produce limb bud defects while RA does. To determine whether TCDD and RA would enhance or antagonize the teratogenic effects of the other compound, C57BL/6N dams were treated po on Gestation Day (gd) 10 or 12 with 10 ml corn oil/kg containing TCDD (0-18 micrograms/kg), RA (0-200 mg/kg), or combinations of the two chemicals. Dams were killed on gd 18 and toxicity and teratogenicity assessed. Coadministration of TCDD and RA had no effect on maternal or fetal toxicity beyond what would be expected by either compound alone. Cleft palate was induced by RA at lower doses on gd 10 than on gd 12, but by TCDD at lower doses on gd 12 than on gd 10. Sensitivity to TCDD-induced hydronephrosis was similar on both gd 10 and 12. The limb bud defects were only observed when RA was administered on gd 10, not when given on gd 12. No other soft tissue or skeletal malformations were related to administration of TCDD or RA. No effect of TCDD was observed on the incidence or severity of limb bud defects induced by RA, nor did RA influence the incidence or severity of hydronephrosis induced by TCDD. However, the incidence of cleft palate was dramatically enhanced by coadministration of the xenobiotic and vitamin. On both gd 10 and 12, the dose-response curves for cleft palate induction were parallel, suggesting some similarities in mechanism between the two compounds. However, combination treatment resulted in a synergistic response that varied with the stage of development and was tissue specific.

Teratogenic effects of polychlorinated dibenzofurans in combination in C57BL6N mice

Abstract Polychlorinated dibenzofurans (PCDFs) are highly toxic environmental contaminants which have been involved in several incidents of human poisoning. Two congeners, 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF) and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF), have been shown to persist in the tissues of victims of accidental ingestion from Japan and Taiwan. The teratogenicity of these compounds, both alone and in combination, was assessed in C57BL 6N mice. Pregnant mice were treated with 10 ml/kg corn oil containing no PCDFs, 4-PeCDF (0–30 μg/kg), HCDF (0–300 μ/kg), or a combination of the two on gestation Days 10–13, followed by necropsy on gestation Day 18. Maternal and fetal toxicity were assessed and selected soft tissues were examined for abnormalities. Both chemicals caused hydronephrosis and cleft palate in the absence of any overt toxicity. Hydronephrosis occurred at doses approximately fivefold lower than those causing cleft palate. The combination of 4-PeCDF and HCDF was additive for terata based on responses predicted by probit analysis. In addition, the combination of 2,3,4,5,3′,4′-hexachlorobiphenyl (0–60 mg/kg), a structurally related compound also present in PCDF poisoning victims, and 4-PeCDF appears additive. Thus, these chemicals, which cause toxic effects similar to those of 2,3,7,8-tetrachlorodibenzo- p -dioxin, are additive in the induction of fetal anomalies in the mouse.

Teratogenicity of three polychlorinated dibenzofurans in C57BL6N mice

Polychlorinated dibenzofurans (PCDFs) are widespread environmental contaminants which have been detected in human tissues and implicated in several poisoning incidents. Their toxic effects are similar to those observed with other related halogenated aromatic hydrocarbons such as TCDD. The teratogenic effects of three PCDFs, 1,2,3,7,8-pentachlorodibenzofuran (1-PeCDF), 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF), and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF), were assessed in C57BL/6N mice. Pregnant mice were exposed on Gestation Days 10-13 to 10 ml corn oil/kg containing PCDFs. The dams were killed on Gestation Day 18 and maternal and fetal toxicity were assessed. All three compounds were highly teratogenic, with very steep and parallel dose-response curves for the two diagnostic indicators of dioxin-like teratogenicity, hydronephrosis, and cleft palate. 4-PeCDF was the most teratogenic with an ED50 of 36 micrograms/kg for cleft palate and 7 micrograms/kg for hydronephrosis. 4-PeCDF was approximately 4 times as potent as 1-PeCDF and 10 times as potent as HCDF. The teratogenic responses occurred at a dose below that where any obvious maternal or fetal toxicity was detected. Thus, these three compounds cause teratogenic responses similar to those seen with TCDD but are only 1/10 to 1/100 as potent.

Teratogenic effects of 2,3,7,8-tetrabromodibenzo-p-dioxin and three polybrominated dibenzofurans in C57BL/6N mice

Brominated flame retardants involved in many industrial uses contain polybrominated dibenzo-p-dioxins (PBDDs) and dibenzofurans (PBDFs) as contaminants. The levels of these contaminants can be dramatically increased by combustion. These chemicals are closely related in structure to the polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs), of which 2,3,7,8-tetrachloridibenzo-p-dioxin (TCDD) is the most toxic isomer. TCDD and related PCDFs are potent mouse teratogens inducing cleft palate and hydronephrosis at doses below those at which overt maternal and embryo/fetal toxicity occurs. This study examines the teratogenic effects of 2,3,7,8-tetrabromodibenzo-p-dioxin (TBDD), 2,3,7,8-tetrabromodibenzofuran (TBDF), 1,2,3,7,8-pentabromodibenzofuran (1PeBDF), and 2,3,4,7,8-pentabromodibenzofuran (4PeBDF) in C57BL/6N mice treated on gestation day (gd) 10 and examined on gd 18. Pregnant dams were treated with 0-4000 micrograms of each congener per kilogram body weight in 10 ml corn oil/kg. Dose selection was based on the relative toxicity of the chlorinated isomers. Maternal toxicity and developmental toxicity were assessed, and the hard palate and kidney, the target organs for the teratogenic effects of TCDD and related compounds, were examined for structural abnormalities. While the maternal liver weight increased at all dose levels examined for all four compounds, there was no evidence of any maternal toxicity. Embryo/fetal mortality was increased only at greater than or equal to 500 microgram TBDF/kg, while fetal weight increased in a dose-related manner following exposure to TBDD and TBDF. All compounds produced hydronephrosis (HN) at doses below that at which cleft palate (CP) occurred. The incidence of HN was significantly increased above background levels at the following doses (micrograms/kg): TBDD, 3; TBDF, 25; 1PeBDF, 500; 4PeBDF, 400. The LOELs (micrograms/kg) for CP were: TBDD, 48; TBDF, 200; 1PeBDF, 4000; 4PeBDF, 2400. The cleft palate incidence for all four brominated compounds and TCDD could be fit to a common slope, compatible with the concept that these chemicals all exert their teratogenic effects through a common mechanism. The potency of these chemicals, relative to TCDD as 1 for the induction of cleft palate, is TBDD, 0.24; TBDF, 0.10; 1PeBDF, 0.004; and 4PeBDF, 0.005. Previous studies from our laboratory had determined that the chlorinated dibenzofuran isomers had relative potencies of 0.05 (TCDF), 0.03 (1PeCDF), and 0.09 (4PeCDF). Thus, bromination decreases the teratogenic activity of TBDD relative to TCDD and of both 1- and 4PeBDF relative to the chlorinated isomers. However, substitution of bromines for chlorines increases the potency of TBDF relative to TCDF.(ABSTRACT TRUNCATED AT 400 WORDS)

Codeine: Developmental Toxicity in Hamsters and Mice

Timed-pregnant LVG Syrian hamsters and Swiss CD-1 mice were dosed orally twice daily (b.i.d.) with codeine in water on Gestational Days (gd) 5-13 (0, 10, 50, or 150 mg/kg, b.i.d.--hamsters) or 6-15 (0, 37.5, 75, 150, or 300 mg/kg, b.i.d.--mice). Dams were necropsied on gd 14 (hamsters) or 17 (mice), and fetuses were weighed, sexed, and examined for external, visceral, and skeletal malformations. No maternal deaths were observed in hamsters, while 19% of the pregnant mice in the high-dose group died. Maternal weight gain (gestational and treatment periods) and gravid uterine weights were significantly depressed in hamsters (150 mg/kg, b.i.d.) and in mice (300 mg/kg, b.i.d.). However, the corrected weight gain for both species, although decreased, was not significantly different from that of the controls. In both species, maternal liver weights (relative) were significantly increased in the high-dose groups. There were increases in the percentage resorptions per pregnant dam and in the proportion of litters with 100% resorptions in the high-dose groups of both species. Considering only live litters, the number of live fetuses per litter and the sex ratio were unaffected in both species. Mean fetal body weights were also significantly decreased in the 50 and 150 mg/kg, b.i.d. (hamsters), and the 150 and 300 mg/kg, b.i.d. (mice), groups. The no-observed-adverse-effect levels (NOAELs) for developmental toxicity were 10 (hamsters) and 75 (mice) mg/kg, b.i.d., whereas the NOAELs for maternal toxicity were 50 (hamsters) and 150 (mice) mg/kg, b.i.d. The predominant structural malformation in hamsters was meningoencephalocele (high-dose group only), affecting 3% of fetuses and 19% of litters (neither statistically significant). Codeine did not induce any increase in structural malformations in mice. Thus, codeine produced developmental toxicity (as indicated by decreased fetal body weight) at doses below those producing maternal toxicity in both hamsters and mice. In the hamster, the more sensitive species to codeine developmental toxicity, effects were observed at a total daily dose of 100 mg/kg, which is only 11 times the maximum human therapeutic oral dose.

Association of sperm, vaginal cytology, and reproductive organ weight data with results of continuous breeding reproduction studies in Swiss (CD-1) mice.

In continuous breeding reproduction studies in which an adverse effect on fertility was detected over an 18-week treatment period, a crossover mating trial was then conducted to determine the affected sex. Results of 25 crossover breeding studies conducted using Swiss (CD-1) mice were compared with results of sperm morphology and vaginal cytology examinations (SMVCEs) conducted at the conclusion of the mating trial. SMVCE endpoints include sperm concentration, motility, and morphology, vaginal cytology, and male reproductive organ weights. In most SMVCE studies multiple endpoints were adversely affected. For male reproductive toxicants, sperm motility was decreased in 89% of the studies, and absolute right epididymis and right testis weights were affected less frequently (80% each). Among studies with no detectable reduction in male breeding performance, 87% exhibited no detectable decrease in epididymis weight. Eighty-two percent had no change in cauda epididymis weight and 80% had no significant change in sperm concentration. An increase in female cycle length was associated (100%) with an effect on breeding due to female dysfunction. Overall accuracy, defined as correct identification of toxicants and nontoxicants, was highest for epididymis weight (84%), followed by cauda epididymis weight and sperm motility (79% each), and sperm concentration (76%). Female cycle length was so variable that the overall accuracy of the parameter in 13 studies was 69%. With the variety of chemicals used in this analysis, the association of abnormal sperm morphology with reproductive outcome was 71%. Control data (mean, 95% confidence interval around the mean, median, and statistical sensitivity) for each male endpoint (parent, and offspring at 10 weeks of age following a single breeding) were summarized from each of the two laboratories that conducted the studies. For several endpoints, statistical power was dependent on the laboratory conducting the studies. In general, the statistical sensitivity was relatively high for reproductive organ weights, although it was less for smaller organs such as the prostate. On the basis of both the biological and statistical analyses, it is recommended that multiple SMVCE endpoints, including sperm measures, be included in screens for reproductive toxicants.