Assessment of female and male fertility in Sprague-Dawley rats administered vorinostat, a histone deacetylase inhibitor

BACKGROUND: Histone deacetylase (HDAC) inhibitors have been shown to mediate the regulation of gene expression, induce cell growth, cell differentiation, and apoptosis of tumor cells. These compounds are now marketed or are in clinical development. One such HDAC inhibitor, vorinostat (suberoylanilide hydroxamic acid [SAHA], Zolinza), was assessed for its potential effects on fertility in Sprague–Dawley rats. METHODS: Female rats were administered oral dose levels of 0 (vehicle only), 15, 50, or 150 mg/kg/day of vorinostat for 14 days before cohabitation, during cohabitation, and through Gestation Day (GD) 7. In a separate study, male rats were administered oral dose levels of 0 (vehicle only), 20, 50, or 150 mg/kg/day for 10 weeks before cohabitation, during cohabitation, and until the day before scheduled sacrifice (approximately 14 weeks total). In both studies, % peri‐implantation loss and % postimplantation loss were evaluated on GD 15–17. Testicular weight and histomorphology, cauda epididymal sperm count, and sperm motility were evaluated in the male rat study at termination. RESULTS: There were treatment‐related decreases in body weight gain at 150 mg/kg/day in both studies. There were no effects on mating or fertility indices in either study. In the female study there were increased numbers of corpora lutea in all drug‐treated groups (only 1 or 2 affected dams in low and mid‐dose groups), and a marked increase in percent postimplantation loss only in the high‐dose group. No treatment‐related effects were observed on litter or sperm parameters of the male study. CONCLUSIONS: Vorinostat had no effects on mating or fertility in rats up to 150 mg/kg/day. There were no indications of reproductive toxicity in drug‐treated male rats. Increases in corpora lutea or resorptions were observed in treated female rats. Birth Defects Res (Part B) 80:1–8, 2007. © 2007 Wiley‐Liss, Inc.     

Developmental toxicity of soman in rats and rabbits

Soman (GD; phosphonofluoridic acid, methyl-,1,2,2-trimethylpropyl ester) is an organophosphate compound with potent anticholinesterase activity. To determine developmental toxicity, soman was administered orally to CD rats on days 6 through 15 of gestation at dose levels of 0, 37.5, 75, 150, or 165 micrograms/kg/day and to New Zealand White (NZW) rabbits on days 6 through 19 of gestation at dose levels of 0, 2.5, 5, 10, or 15 micrograms/kg/day. At sacrifice, gravid uteri were weighed and examined for number and status of implants. Individual fetal body weights and external, visceral, and skeletal malformations were recorded. Mean maternal weight changes, fetal implantation status/litter, fetal weight, and fetal malformations/litter were compared between dose groups. Monitors for maternal toxicity were net body weight change, treatment weight change, mortality, and clinical signs of toxicity such as lethargy, ataxia, and tremors. Maternal rats and rabbits in the high-dose groups exhibited statistically significant increases in toxicity and mortality when compared to controls. There were no significant dose-related effects among dose groups in the prevalence of postimplantation loss, malformations, or in average body weight of live fetuses per litter. There was no evidence of increased prenatal mortality or fetal toxicity in the CD rat or NZW rabbit following exposure to soman, even at a dose that produced significant maternal toxicity.     

Developmental toxic effects of antifungal flusilazole administered by gavage to mice

BACKGROUND: The developmental toxicity of flusilazole was studied in CD-1 mice after oral administration. METHODS: Pregnant mice were given flusilazole at doses of 0 (corn oil), 10, 20, and 40 mg/kg/day, by gavage, on gestational days (GD) 6-15. RESULTS: Maternal toxicity, as evidenced by reduction in body weight gain and signs of toxicity, was observed at the middle- and high-dose groups. No significant incidence of resorptions or death was observed in any of dose groups. There was a pronounced reduction in fetal weight, which was significantly lower than control from 20 and 40 mg/kg/day. There was no significant increase in the incidence of fetuses with external or visceral malformations in any of dose groups, but there was a significant increase in the incidence of skeletal malformations was observed at 20 and 40 mg/kg/day. CONCLUSIONS: The results of this study reported marked maternal toxicity, growth retardation, and skeletal abnormalities in the mid- and high-dose groups. It seems likely that marked maternal toxicity contributed to the observed alterations in fetal growth retardation and skeletal development. The no-observed-effect level in the present study for maternal and developmental toxicity was 10 mg/kg/day.     

Developmental toxicity of pentostatin (2'-deoxycoformycin) in rats and rabbits

The developmental toxicity of the potent adenosine deaminase (ADA) inhibitor, pentostatin (2'-deoxycoformycin), was investigated in pregnant rats and rabbits administered daily iv doses during organogenesis. Rats received 0, 0.01, 0.10, or 0.75 mg/kg on gestation days 6-15 and rabbits received 0, 0.005, 0.01, or 0.02 mg/kg on gestation days 6-18 and maternal and fetal parameters were evaluated on gestation day 21 (rats) or 30 (rabbits). Live fetuses were examined for external, visceral, and skeletal malformations and variations. In rats, maternal body weight gain and food consumption were significantly suppressed at doses of 0.10 and 0.75 mg/kg during the treatment period but returned to control levels during posttreatment. Increased postimplantation loss and decreased numbers of live fetuses, litter size, and fetal body weight were observed at 0.75 mg/kg. A statistically significant increase in the incidence of vertebral malformations occurred at 0.75 mg/kg. The incidence of certain skeletal variations (extra presacral vertebrae, extra ribs, hypoplastic vertebrae) was also increased at 0.75 mg/kg. Ossification of cervical centra was reduced at 0.75 mg/kg compared with controls. In rabbits, marked maternal toxicity (death, body weight loss, and decreased food consumption) and reproductive toxicity (abortion and premature delivery) occurred in all pentostatin-treated groups. However, there were no significant effects on number of live fetuses, pre- or postimplantation loss, litter size, or fetal body weights in the animals with live litters. There was also no apparent increase in the incidence of malformations or variations in the live fetuses of pentostatin-treated rabbits. Thus, these studies demonstrate developmental toxicity of pentostatin in rats and rabbits, and teratogenicity in rats, at maternally toxic doses.     

Different embryo-fetal toxicity effects for three VLA-4 antagonists

BACKGROUND: VLA‐4 (Very late antigen 4, integrin α₄β₁) plays an important role in cell‐cell interactions that are critical for development. Homozygous null knockouts of the α₄subunit of VLA‐4 or VCAM‐1 (cell surface ligand to VLA‐4) in mice result in abnormal placental and cardiac development and embryo lethality. Objectives of the current study were to assess and compare the teratogenic potential of three VLA‐4 antagonists. METHODS: IVL745, HMR1031, and IVL984 were each evaluated by the subcutaneous route in standard embryo‐fetal developmental toxicity studies in rats and rabbits. IVL984 was also evaluated in mice. Fetuses were examined externally, viscerally, and skeletally. RESULTS: IVL745 did not cause significant maternal or fetal effects at doses up to 100 or 250 mg/kg/day in rats or rabbits, respectively. HMR1031 treatment resulted in marked maternal toxicity and slight fetal toxicity at the highest tested doses of 200 and 75 mg/kg/day in rats and rabbits, respectively. HMR1031 embryo‐fetal effects consisted of slightly lower body weight and crown‐rump length in rats and minor sternebral defects in rabbits. IVL984 treatment resulted in minimal maternal effects at doses up to 40, 15, and 100 mg/kg/day in rats, rabbits, and mice, respectively (excluding abortions in rabbits). However, marked developmental effects were observed at the lowest tested IVL984 doses, 1, 0.2, and 3 mg/kg/day in rats, rabbits, and mice, respectively. IVL984 embryo‐fetal effects consisted of increased total post‐implantation loss due to early resorptions and high incidences of cardiac malformations and skeletal malformations and/or variations. Notably, spiral septal defects were observed in up to 76% of rat fetuses and up to 58% of rabbit fetuses. CONCLUSIONS: Dramatic differences in teratogenic potential were observed: IVL745 was not teratogenic, HMR1031 caused slight embryo‐fetal effects at maternally‐toxic doses, and IVL984 was a potent teratogen at doses where direct maternal toxicity was limited to abortions in rabbits. Prominent effects of IVL984 included embryo lethality and cardiac malformations including spiral septal defects in three species. Birth Defects Res B 71:55–68, 2004. © 2004 Wiley‐Liss, Inc.     

Developmental Toxicity of the HMG‐CoA Reductase Inhibitor (PPD10558) in Rats and Rabbits

PPD10558 is an orally active, lipid‐lowering 3–hydroxy‐3‐methylglutaryl coenzyme A (HMG‐CoA) reductase inhibitor (statin) being developed as a treatment for hypercholesterolemia in patients who have not been able to tolerate statins because of statin‐associated myalgia. We have studied the potential developmental toxicity effects of PPD10558 in pregnant rats and rabbits given daily oral doses during the period of organogenesis. Rats were dosed with 0, 20, 80, or 320 mg/kg/day from Gestation Day (GD) 6 to 17 and rabbits received dose levels of 0, 12.5, 25, or 50 mg/kg/day from GD 6 to 18. Additional groups in both studies served as toxicokinetic animals and received the PPD10558 in the same manner as the main study groups at the same dose levels. Blood samples were collected from toxicokinetic animals at designated time points on GD 6 and 17 in rats and GD 6 and 18 in rabbits. Fetal exposure in rats was assessed on GD 20. Maternal and developmental parameters were evaluated in rats and rabbits on GD 20 and GD 29, respectively. No maternal and developmental toxicity was observed at any of the dose levels used in the rat study. Evidence of fetal exposure was determined in fetal plasma with mean fetal concentrations of PPD10558 and the metabolite (PPD11901) found to be between 1 and 6% of the mean maternal concentrations. In rabbits, marked maternal toxicity including mortality (eight deaths; 1 dose at 25 and 7 at 50 mg/kg/day), abortions (2 at 25 mg/kg/day and 6 at 50 mg/kg/day) and reduction in gestation body weight, gestation body weight changes and decreased food consumption were observed. In addition, fetal body weights of the combined sexes were significantly reduced at 50 mg/kg/day in comparison with the controls. Mean peak exposure (Cmax) and total exposure (AUC(0–24)) of PPD11901 in both rats and rabbits were higher than that of PPD10558 on GD 6 and GD 17 at each of the three dose levels.. Based on the results of these studies, the no observed adverse effect level (NOAEL) for maternal and developmental toxicity in rats was considered to be ≥320 mg/kg/day, the highest dose level used in the study. The NOAEL for maternal and developmental toxicity in rabbits was 12.5 mg/kg/day and 25 mg/kg/day, respectively.     

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.     

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.     

Evaluation of the safety and pharmacokinetics of the multi-targeted receptor tyrosine kinase inhibitor sunitinib during embryo–fetal development in rats and rabbits

BACKGROUND : Angiogenesis plays a key role in embryo–fetal development and, based on nonclinical safety data, the majority of vascular endothelial growth factor (VEGF)-targeted antiangiogenic agents used in cancer therapy are not recommended during pregnancy. We investigated the effects of sunitinib (an oral inhibitor of multiple receptor tyrosine kinases [RTKs] including VEGF-receptors) on embryo–fetal development. METHODS : Presumed-pregnant Sprague-Dawley rats and New Zealand White rabbits received repeated daily oral doses of sunitinib (0–30 mg/kg/day), during the major period of organogenesis. Clinical/physical examinations were performed throughout the gestation phase, and blood samples were collected to determine systemic exposure. Necropsy (including uterine examination) was performed on all animals and fetal morphology was examined. RESULTS : The no-observed-adverse-effect level was 1–5 mg/kg/day for maternal toxicity and 3 mg/kg/day for developmental toxicity in rats; 1 and 0.5 mg/kg/day, respectively, in rabbits. Embryo–fetal toxicity included decreases in the number of live fetuses and increases in the numbers of resorptions and post-implantation/complete litter losses; these were observed at doses of ≥5 mg/kg/day in rats and 5 mg/kg/day in rabbits. Malformations included fetal skeletal malformations (generally thoracic/lumbar vertebral alterations) in rats and cleft lip/palate in rabbits. These developmental effects were observed at ∼5.5- (rats) and ∼0.3-times (rabbits) the human systemic exposure at the approved sunitinib dose (50 mg/day). CONCLUSIONS : Similar effects have been reported with the prototype monoclonal antibody bevacizumab. As is typically observed for potent inhibitors of RTKs involved in angiogenesis, sunitinib was associated with embryo–fetal developmental toxicity in rats and rabbits at clinically relevant dose levels. Birth Defects Res (Part B) 33:204–213, 2009. © 2009 Wiley-Liss, Inc.     

Developmental toxicity evaluation of sodium thioglycolate administered topically to Sprague-Dawley (CD) rats and New Zealand White rabbits

BACKGROUND: Sodium thioglycolate, which has widespread occupational and consumer exposure to women from cosmetics and hair‐care products, was evaluated for developmental toxicity by topical exposure during the embryonic and fetal periods of pregnancy METHODS: Timed‐mated Sprague–Dawley rats (25/group) and New Zealand White (NZW) rabbits (24/group) were exposed to sodium thioglycolate in vehicle (95% ethanol:distilled water, 1:1) by unoccluded topical application on gestational days (GD) 6–19 (rats) or 6–29 (rabbits) for 6 hr/day, at 0, 50, 100, or 200 mg/kg body weight/day (rats) and 0, 10, 15, 25, or 65 mg/kg/day (rabbits). At termination (GD 20 rats; GD 30 rabbits), fetuses were examined for external, visceral, and skeletal malformations and variations. RESULTS: In rats, maternal topical exposure to sodium thioglycolate, at 200 mg/kg/day (the highest dose tested) on GD 6–19, resulted in maternal toxicity, including reduced body weights and weight gain, increased relative water consumption and one death. Treatment‐related increases in feed consumption and changes at the application site occurred at all doses, in the absence of increased body weights or body weight change. Fetal body weights/litter were decreased at 200 mg/kg/day, with no other embryo/fetal toxicity and no treatment‐related teratogenicity in any group. In rabbits, maternal topical exposure to sodium thioglycolate on GD 6–29 resulted in maternal dose‐related toxicity at the dosing site in all groups; no maternal systemic toxicity, embryo/fetal toxicity, or treatment‐related teratogenicity were observed in any group. CONCLUSIONS: A no observed adverse effect level (NOAEL) was not identified for maternal toxicity in either species with the dosages tested. The developmental toxicity NOAEL was 100 mg/kg/day (rats) and ≥65 mg/kg/day (rabbits; the highest dose tested). The clinical relevance of theses study results is uncertain because no data were available for levels, frequency, or duration of exposures in female workers or end users. Birth Defects Research Part B 68:144–161, 2003. © 2003 Wiley‐Liss, Inc.     

Influence of maternal stress on uranium-induced developmental toxicity in rats

It has been demonstrated that uranium is an embryo/fetal toxicant when given orally or subcutaneously to pregnant mice. On the other hand, maternal stress has been shown to enhance the developmental toxicity of a number of metals. In this study, maternal toxicity and developmental effects of a concurrent exposure to uranyl acetate dihydrate (UAD) and restraint stress were evaluated in rats. Four groups of pregnant animals were given subcutaneous injections of UAD at 0.415 and 0.830 mg/kg/day on Days 6 to 15 of gestation. Animals in two of these groups were also subjected to restraint for 2 hr/day during the same gestational days. Control groups included restrained and unrestrained pregnant rats not exposed to UAD. Cesarean sections were performed on gestation Day 20, and the fetuses were weighed and examined for malformations and variations. Maternal toxicity and embryotoxicity were noted at 0.830 mg/kg/day of UAD, while fetotoxicity was evidenced at 0.415 and 0.830 mg/kg/day of UAD by significant reductions in fetal body weight and increases in the total number of skeletally affected fetuses. No teratogenic effects were noted in any group. Maternal restraint enhanced uranium-induced embryo/fetal toxicity only at 0.830 mg/kg/day, a dose that was also significantly toxic to the dams. As in previous studies with other metals, maternal stress enhances uranium-induced developmental toxicity at uranium doses that are highly toxic to the dams; however, at doses that are less acutely toxic the role of maternal stress would not be significant.     

The role of maternal toxicity in lovastatin-induced developmental toxicity

The role of maternal toxicity in lovastatin-induced developmental toxicity in rats was examined in a series of studies. The first study administered lovastatin at 100, 200, 400, or 800 mg/kg/day (mkd) orally to mated rats from Gestation Day (GD) 6 through 20. Maternal toxicity was observed as transient dose-related body weight losses at the initiation of dosing; there were also deaths and/or morbidity at 400 and 800 mkd. These toxicities occurred in conjunction with forestomach lesions. Mean fetal weights were decreased in all groups (-5 to -16%), and the incidence of skeletal malformations, variations, and incomplete ossifications was increased. The 2 highest doses produced the most severe maternal and developmental effects. Using the same dosages, the second study avoided gestational maternal weight losses and morbidity by starting treatment 14 days before mating with dosing continued to GD 20. There were transient dose-related body weight losses after the start of dosing and deaths in the 400- and 800-mkd groups; however, there was no evidence of maternal toxicity during gestation. Developmental toxicity was evident only as slight, but generally significant (p< or =0.05) decreases in mean fetal weights in groups given > or =200 mkd (-2 to -5%). Significantly, no skeletal abnormalities were observed. A third study administered the pharmacologically active metabolite of lovastatin subcutaneously at dose levels that matched oral maternal drug exposures. In the high-dose group, maternal weight gain and mean fetal weight were slightly decreased but there were no treatment-related skeletal abnormalities. Finally, a series of toxicokinetic studies assessed whether the 2 different developmental toxicity profiles were due to differences in drug exposure between the developmentally toxic and non-toxic dosing regimes. The data showed that groups with no skeletal abnormalities had maternal and embryonic/fetal drug concentrations similar to or even greater than the groups with fetal abnormalities. These results indicate that fetal skeletal abnormalities observed at lovastatin dose levels > or =100 mkd are not due to a direct teratogenic effect, but are the result of excessive maternal toxicity, which most likely involves a nutritional deficiency associated with forestomach lesions and reduced maternal food intake.     

Developmental and reproductive toxicity studies on artemisone

BACKGROUND: In order to justify clinical studies in women of child-bearing age with artemisone, a new artimisinin derivative, studies to assess fertility and early embryonic development in rats, developmental toxicity in rats and rabbits, and peri-post natal development in rats were performed. METHODS AND RESULTS: In the study on fertility and early embryonic development (dose levels 0-5-20-80 mg/kg bw/day), doses inducing clinical and organ toxicity were used. Only in severe toxicity conditions, a reduction of the number of estruses, a prolonged time to insemination, decreased numbers of corpora lutea, implantation sites, and viable fetuses were found. Two developmental toxicity studies were performed in rats (dose levels 0-1-2 mg/kg bw/day) and rabbits (dose levels 0-2.5-5.0-7.5 mg/kg bw/day). It was shown that rats were about 5 times more sensitive than rabbits. In rats, artemisone induced total litter loss (late resorptions) at 2 mg/kg body weight and above with an increased incidence of a common vascular variation and retarded ossification at this dose. In rabbits, maternal toxicity, abortion and a slightly increased incidence of cardiac ventricular septal defects was observed at 7.5 mg/kg body weight. In a pre- and postnatal developmental toxicity study in rats (dose levels 0-1-2-4 mg/kg bw/day), 4 mg/kg body weight artemisone induced clinical symptoms and affected postnatal survival, body weight gain in the F1 pups, and motor activity. CONCLUSIONS: In summary, artemisone was shown to be embryo- and fetotoxic and induced cardiac ventricular septal defects and retarded ossification in dosages where total litter loss and abortions were observed. However, no effect on reproductive and developmental parameters below severe toxic dosages could be observed. Birth Defects Res (Part B)86: 131-143, 2009. © 2009 Wiley-Liss, Inc.     

D-methylphenidate and D,L-methylphenidate are not developmental toxicants in rats and rabbits

BACKGROUND: D ,L ‐threo‐Methylphenidate (D ,L ‐MPH) is marketed currently for attention deficit hyperactivity disorder in children. D ‐threo‐methylphenidate (dexmethylphenidate; D ‐MPH) is a refined formulation of D ,L ‐methylphenidate containing only the active enantiomer and was recently approved in the U.S. for the same condition. D ‐Methylphenidate has been shown to be efficacious in patients at half the dose of D ,L ‐MPH with a potentially improved therapeutic profile. The developmental toxicity of both compounds was determined and compared in rats and rabbits according to current International Conference on Harmonization (ICH) guidelines. METHODS: Groups of pregnant rats were orally dosed twice daily 6 hr apart from Days 7 to 17 of presumed gestation (DG 7–17) for total daily doses of 2, 6 and 20 mg/kg D ‐MPH and 40 mg/kg D ,L ‐MPH. Groups of presumed pregnant rabbits were similarly dosed from DG 6 to 18 for total daily doses of 4, 20 and 100 mg/kg D ‐MPH and 200 mg/kg D ,L ‐MPH. Control groups for both studies were given water vehicle. Comprehensive clinical and developmental measurements were made. Satellite groups of animals were included in the main rat and rabbit studies for toxicokinetic assessment. RESULTS: No drug‐related mortality was seen in the F0 rats and rabbits. The number of rats with repetitive pawing, dilated pupil and aggression was significantly greater for the 40 mg/kg D ,L ‐MPH compared to the 20 mg/kg D ‐MPH dosed rats. Maternal body weight and body weight gain were significantly reduced for both D ‐MPH and D ,L ‐MPH groups compared to control. Maternal reproductive and litter parameters were unaffected by both drugs. No gross external, soft tissue, or skeletal alterations related to both compounds were seen in the fetuses. In rabbits, head‐bobbing and hyperpnea were significantly greater for the 200 mg/kg D ,L ‐MPH compared to 100 mg/kg D ‐MPH. No other maternal or fetal effects related to both compounds were seen. Exposure to D ‐MPH (as assessed by AUC) showed no teratogenic effects at exposures of up to 5.6 and 1.7 times for the rat and rabbit respectively compared to children taking the maximum therapeutic dose of 20 mg/day (10 mg twice a day). No teratogenic effects were seen for D ,L ‐MPH in rat and rabbit at exposures of up to 3.7 to 11.7 times that of the maximum therapeutic pediatric dose of 60 mg/day. CONCLUSIONS: Rats and rabbits dosed with D ,L ‐MPH exhibited significantly greater incidence of maternal clinical observations at twice the dose of D ‐MPH. Both D ‐MPH and D ,L ‐MPH were not teratogenic in rats and rabbits at higher exposure levels compared to humans. © 2003 Wiley‐Liss, Inc.     

Prenatal developmental toxicity of decabromodiphenyl ethane in the rat and rabbit

BACKGROUND: The potential embryotoxic and teratogenic effects of decabromodiphenyl ethane (DBDPEthane; CASRN 84852–53–9) were evaluated in prenatal developmental studies using rats and rabbits and performed in accordance with international guidelines and Good Laboratory Practice standards. Preliminary dose‐range‐finding studies were conducted, which indicated doses up to 1,250 mg/kg‐day were well tolerated by both rats and rabbits. METHODS: For the developmental studies, animals were administered DBDPEthane via gavage at dosage levels of 0, 125, 400, or 1,250 mg/kg‐day from gestation day (GD) 6 through 15 for rats and GDs 6 through 18 for rabbits. All female rats and rabbits were sacrificed on GD 20 or GD 29, respectively, and subjected to cesarean section. Fetuses were individually weighed, sexed, and examined for external, visceral and skeletal abnormalities. RESULTS: No treatment‐related mortality, abortions, or clinical signs of toxicity were observed during the study. Body weights, body weight gain, and food consumption were not affected by treatment. No significant internal abnormalities were observed in either species on necropsy. Cesarean section parameters were comparable between control and treated groups. No treatment‐induced malformations or developmental variations occurred. CONCLUSIONS: Based on these results, no evidence of maternal toxicity, developmental toxicity, or teratogenicity was observed in rats or rabbits treated with DBDPEthane at dosage levels up to 1,250 mg/kg‐day. Birth Defects Res (Part B) 89:139–146, 2010. © 2010 Wiley‐Liss, Inc.     

Developmental toxicity of 1,6-hexamethylene diisocyanate (HDI) in the Sprague-Dawley rat

BACKGROUND: 1,6-Hexamethylene diisocyanate (HDI), a widely used chemical in commercial polyurethane manufacture, has been shown to affect the respiratory tract of experimental animals. However, its potential to affect neonatal development, particularly after inhalation exposure, is less well described. The present study was conducted to assess the developmental toxicity of HDI. METHODS: Gravid Sprague-Dawley rats were exposed to concentrations of 0, 0. 005, 0.050, or 0.300 ppm HDI via inhalation (whole-body exposure) on days 0-19 of gestation. Maternal toxicity, as demonstrated by clinical signs and changes in body weight gain during gestation, was characterized. Dams were sacrificed on gestation day 20, at which time fetuses were removed by cesarean section, the uterus was examined, and a gross maternal necropsy was performed. Maternal evaluation also included lung weight and a detailed histopathologic assessment of the nasal turbinates, larynx, trachea, and lungs. All fetuses were evaluated for external anomalies. Approximately one-half of each litter was examined for visceral effects, the other half underwent a skeletal (bone and cartilage) examination. RESULTS: Maternal toxicity was demonstrated in the 0.300- and, to a lesser extent, in the 0.050-ppm exposure groups. No maternal effects were noted in the 0.005-ppm group. Test compound-related maternal effects were restricted to histopathological findings and included acanthosis, hyperkeratosis, inflammation of the nasal turbinates, and, more seriously, degeneration of the olfactory epithelium. No pathological alterations were noted in the larynx, trachea, or lungs in any dose group. No test compound-related effects were observed on any reproductive parameters, or any embryonic endpoints, including pre/postimplantation loss and resorption. There were no effects on litter size or the number of fetuses per implantation site and no effects on fetal or placental weights were observed. No test compound-related fetal external, visceral, or skeletal findings were observed. No effect on the fetal or litter incidence of total malformations or variations was observed, and there was no difference in the incidence of malformations between males and females. CONCLUSIONS: Administered as described in this study, 1, 6-HDI produced maternal effects (nasal turbinate histopathology) at concentrations of 0.050 and 0.300 ppm with no developmental toxicity observed at any concentration.     

Developmental toxicity evaluation of trimethylolpropane caprylate caprate in Sprague-Dawley rats

The developmental toxicity potential of trimethylolpropane caprylate caproate (TMPCC, CAS no. 11138-60-6) was evaluated in rats. Sprague-Dawley rats were administered TMPCC in a corn oil suspension dermally at dose levels of 0, 200, 600, or 2,000 mg/kg/day on gestation days (GD) 6-15 (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 22 per group being pregnant. The two highest dose levels caused some local irritation at the site of application, but no decreases in maternal weight gain. There were no differences from control in any of the developmental parameters measured, including embryo/fetal viability, fetal weight, malformations, or variations. TMPCC did not cause any developmental toxicity in the Sprague-Dawley rat at dermal dosages up to 2,000 mg/kg/day.     

Developmental toxicity of artesunate and an artesunate combination in the rat and rabbit

The artemisinins are playing an increasingly important role in treating multidrug-resistant malaria. The artemisinin, artesunate, is currently in use in Southeast Asia and is advocated for use in Africa. In these areas, more than one million people die of malaria each year, with the highest mortality occurring in children and pregnant women. To test the developmental toxicity in ICH-compliant animal studies, embryofetal development studies were conducted in rats and rabbits treated with artesunate alone or a three-drug combination (CDA) consisting of chlorproguanil hydrochloride, Dapsone, and artesunate in the ratio 1.00:1.25:2.00. Developmental toxicity seen with CDA could be attributed to the administered dose of artesunate. The hallmark effect of artesunate exposure was a dramatic induction of embryo loss, apparent as abortions in rabbits and resorptions in both rats and rabbits. In addition, low incidences of cardiovascular malformations and a syndrome of skeletal defects were induced at or close to embryolethal doses of artesunate in both rats and rabbits. The cardiovascular malformations consisted of ventricular septal and vessel defects. The skeletal syndrome consisted of shortened and/or bent long bones and scapulae, misshapen ribs, cleft sternebrae, and incompletely ossified pelvic bones. These developmental effects were observed largely in the absence of any apparent maternal toxicity. The no or low adverse effect levels were in the range of 5 to 7 mg/kg/day artesunate. Encouragingly, no adverse drug-related developmental effects have been observed in a limited number of pregnant women (more than 100 first trimester and 600 second and third trimester) treated with artemisinins, primarily artesunate. Investigations of the mechanism of developmental toxicity are ongoing to attempt to determine whether rats and rabbits are more sensitive to artemisinins than humans.     

TGF‐β1 monoclonal antibody: Assessment of embryo‐fetal toxicity in rats and rabbits

A humanized monoclonal antibody targeting transforming growth factor β1 (TGF‐β1 mab) has been used in development for the treatment of chronic kidney disease. Embryo‐fetal development studies were conducted in rats and rabbits using 30 and 25 animals per group, respectively. The TGF‐β1 mab was administered subcutaneously to rats at 0, 2, or 50 mg/kg/dose on gestation days (GDs) 6, 10, and 14 and intravenously to rabbits at 0 or 3 mg/kg/dose on GDs 7, 12 to 19, and at 30 mg/kg/dose on GDs 7, 12, 14, 16, and 18. Maternal reproductive endpoints and fetal viability, weight, and morphology were evaluated. There was no indication of maternal or embryo‐fetal toxicity in the rat. Effects in the rabbit were limited to the fetus where the 30 mg/kg TGF‐β1 mab dose produced a slight decrease in fetal weight and an increase in the incidence of retrocaval ureter and an absent and/or malpositioned kidney/ureter in two fetuses. In conclusion, TGF‐β1 mab produced no adverse maternal or embryo‐fetal findings in rats when administered ≤50 mg/kg on GDs 6, 10, and 14. TGF‐β1 mab did not demonstrate maternal toxicity or embryo‐fetal lethality at doses as high as 30 mg/kg when administered on GDs 7, 12, 14, 16, and 18 in rabbits. Fetal growth and morphology were affected only at 30 mg/kg; thus, the no observed adverse effect level was 3 mg/kg in rabbits. The margin of safety for both rats and rabbits was ≥37‐fold the clinical exposure level.