Absence of prenatal developmental toxicity from inhaled arsenic trioxide in rats.

A review of the literature revealed no published inhalational developmental toxicity studies of arsenic performed according to modern regulatory guidelines and with exposure throughout gestation. In the present study, inorganic arsenic, as arsenic trioxide (As(+3), As2O3), was administered via whole-body inhalational exposure to groups of twenty-five Crl:CD(SD)BR female rats for six h per day every day, beginning fourteen days prior to mating and continuing throughout mating and gestation. Exposures were begun prior to mating in order to achieve a biological steady state of As(+3) in the dams prior to embryonal-fetal development. In a preliminary exposure range-finding study, half of the females that had been exposed to arsenic trioxide at 25 mg/m3 died or were euthanized in extremis. In the definitive study, target exposure levels were 0.3, 3.0, and 10.0 mg/m3. Maternal toxicity, which was determined by the occurrence of rales, a decrease in net body weight gain, and a decrease in food intake during pre-mating and gestational exposure, was observed only at the 10 mg/m3 exposure level. Intrauterine parameters (mean numbers of corpora lutea, implantation sites, resorptions and viable fetuses, and mean fetal weights) were unaffected by treatment. No treatment-related malformations or developmental variations were noted at any exposure level. The no-observed-adverse-effect level (NOAEL) for maternal toxicity was 3.0 mg/m3; the NOAEL for developmental toxicity was greater than or equal to 10 mg/m3, 760 times both the time-weighted average threshold limit value (TLV) and the permissible exposure limit (PEL) for humans. Based on the results of this study, we conclude that arsenic trioxide, when administered via whole-body inhalation to pregnant rats, is not a developmental toxicant.     

Subchronic, reproductive, and developmental toxicity of a fluorotelomer-based urethane polymeric product

A commercial fluorotelomer-based urethane polymeric dispersion, consisting of polymer, surfactant, and water, was evaluated in subchronic, reproduction, and developmental toxicity studies. The dispersion was administered daily by gavage to rats at dosages of 0, 50, 250, or 1000 mg polymer/kg/day or with 70 mg/kg/day of the sulfonate surfactant. Dose levels of 0, 50, 250, or 1000 mg polymer/kg/day were also used for the reproductive and developmental studies. Nasal olfactory epithelial degeneration and necrosis occurred in all dose groups in the 90-day study. Nasal adhesions were observed only in rats administered surfactant alone. Liver-enzyme alterations at 250 and 1000 mg/kg were considered to be potentially adverse effects. The subchronic no-observed-adverse-effects level (NOAEL) was 50 mg/kg. For the reproduction study, rats were dosed for 10 weeks prior to cohabitation and throughout mating, gestation, and lactation. There were no effects on reproductive function in males or females at any dosage. Thyroid weight was decreased in the 250 and 1000 mg/kg day F(1) groups unaccompanied by microscopic effects. In the developmental toxicity study, female rats were dosed from gestation days 6-20; there was no test-substance-related embryolethality, nor was there any dose-related increase in either fetal malformations. Fetal weight was minimally decreased at 1000 mg/kg/day in the presence of slight maternal toxicity; the NOAEL for developmental parameters was 250 mg/kg/day. The polymeric product was not a specific developmental or reproductive toxin.     

Subchronic,Reproductive, and Developmental Toxicity of a Fluorotelomer-Based Urethane Polymeric Product

A commercial fluorotelomer-based urethane polymeric dispersion, consisting of polymer, surfactant, and water, was evaluated in subchronic, reproduction, and developmental toxicity studies. The dispersion was administered daily by gavage to rats at dosages of 0, 50, 250, or 1000 mg polymer/kg/day or with 70 mg/kg/day of the sulfonate surfactant. Dose levels of 0, 50, 250, or 1000 mg polymer/kg/day were also used for the reproductive and developmental studies. Nasal olfactory epithelial degeneration and necrosis occurred in all dose groups in the 90-day study. Nasal adhesions were observed only in rats administered surfactant alone. Liver-enzyme alterations at 250 and 1000 mg/kg were considered to be potentially adverse effects. The subchronic no-observed-adverse-effects level (NOAEL) was 50 mg/kg. For the reproduction study, rats were dosed for 10 weeks prior to cohabitation and throughout mating, gestation, and lactation. There were no effects on reproductive function in males or females at any dosage. Thyroid weight was decreased in the 250 and 1000 mg/kg day F₁ groups unaccompanied by microscopic effects. In the developmental toxicity study, female rats were dosed from gestation days 6–20; there was no test-substance-related embryolethality, nor was there any dose-related increase in either fetal malformations. Fetal weight was minimally decreased at 1000 mg/kg/day in the presence of slight maternal toxicity; the NOAEL for developmental parameters was 250 mg/kg/day. The polymeric product was not a specific developmental or reproductive toxin.     

Developmental toxicity assessment of arsenic acid in mice and rabbits

To evaluate potential effects of exposure to inorganic arsenic throughout major organogenesis, CD-1 mice and New Zealand White rabbits were gavaged with arsenic acid dosages of 0, 7.5, 24, or 48 mg/kg/d on gestation days (GD) 6 through 15 (mice) or 0, 0.19, 0.75, or 3.0 mg/kg/d on GD 6 through 18 (rabbits) and examined at sacrifice (GD 18, mice; GD 29, rabbits) for evidence of toxicity. Two high-dose mice died, and survivors at the high and intermediate doses had decreased weight gains. High-dose-group fetal weights were decreased; no significant decreases in fetal weight or increases in prenatal mortality were seen at other dosages. Similar incidences of malformations occurred in all groups of mice, including controls. At the high dose in rabbits, seven does died or became moribund, and prenatal mortality was increased; surviving does had signs of toxicity, including decreased body weight. Does given lower doses appeared unaffected. Fetal weights were unaffected by treatment, and there were no effects at other doses. These data revealed an absence of dose-related effects in both species at arsenic exposures that were not maternally toxic. In mice, 7.5 mg/kg/d was the maternal No-Observed-Adverse-Effect-Level (NOAEL); the developmental toxicity NOAEL, while less well defined, was judged to be 7.5 mg/kg/d. In rabbits, 0.75 mg/kg/d was the NOAEL for both maternal and developmental toxicity.     

Study of the teratogenic potential of FD & C Yellow No. 5 when given by gavage to rats

FD & C Yellow No. 5 (tartrazine) was given to Osborne-Mendel rats by gavage at dose levels of 0, 60, 100, 200, 400, 600 or 1000 mg/kg body weight/day on days 0–19 of gestation. No maternal or developmental toxicity was observed when the rats were killed on day 20. The mean daily food consumption for the entire period of gestation was significantly greater in the females given 1000 mg/kg body weight/day than in the controls, but maternal body-weight gain was not affected. No dose-related effects were observed in implantations, foetal viability or external foetal development. Foetal skeletal and visceral development was similar among foetuses from all groups. At the doses given, FD & C Yellow No. 5 was neither toxic nor teratogenic.     

Reproductive and Developmental Toxicity Studies of a Linear Alkylbenzene Mixture in Rats

Alkylate 215, a mixture of linear decyl- to tridecylbenzenes,is an intermediate in the manufacture of detergent sulfonates.A two-generation reproduction study and a developmental toxicitystudy were conducted using single daily doses given by gastricintubation in a corn oil vehicle. In the reproduction study,groups of 30 rats/sex/group were given doses of 0, 5, 50, or500 mg/kg/day. F₀ animals received a 10-week premating treatmentperiod and were then mated to produce a single litter; F₁ adultswere selected from the F₁ litters. F₁ animals were dosed for11 weeks before mating to produce a single litter. Adults andweaned pups received a gross postmortem examination. Histopathologystudies were conducted on reproductive tissues, tissues withgross lesions, and the pituitary gland taken from each adultin the control and high dose groups. In the developmental toxicitystudy, groups of 24 mated female rats were given 0, 125, 500,or 2000 mg/kg/day on Days 6 through 15 of gestation. Dams wereterminated on gestation Day 20 and fetuses were examined forexternal, soft tissue, and skeletal defects. Results of thereproduction study were as follows. At 50 mg/kg/day, pup weightswere decreased at Day 7 in the F₁ litter. At 500 mg/kg/day,decreases were found in the F₁ females in premating and earlylactation weight gains; in both generations in premating weightgains in males and in weight gains during gestation in females;and in litter size, pup viability at birth, Day 0–4 sur vival, and pup weights on Days 14 and 21. The NOAEL for reproductiveeffects was 5 mg/kg/day. The developmental toxicity study foundeffects on several parameters. The only effect noted at 125mg/kg/day was a slight decrease in maternal weight gain. Maternalweight gains were depressed to a greater extent at 500 and 2000mg/kg/day. Ossification variations and delayed ossificationwere increased significantly at 2000 mg/kg/day and were abovecontrol levels at 500 mg/kg/day. The NOAEL for developmentaltoxicity was 125 mg/kg/day. Alkylate 215 did not have any unusualor selective reproductive or developmental toxicity.     

Developmental toxicity of thiodiglycol in Sprague-Dawley rats

Thiodiglycol (TG), a hydrolysis product of sulfur mustard (HD), is a potential contaminant of soil and water at certain military sites. To establish developmental toxicity criteria for TG, an oral developmental toxicity study was conducted in Sprague-Dawley rats. Neat thiodiglycol (99.9 %) was administered orally to mated female rats from gestation days (GDs) 5 through 19. The day of positive mating was considered day 0. A pilot study was conducted with TG at dose levels 250, 500, 1,000, 2,000, or 5,000 mg/kg to select suitable doses for the main study. In the main study, three groups of rats (25/group) received TG by gavage at dose levels of 430, 1,290, or 3,870 mg/kg/day. A fourth group served as a sham control. On day 20 of gestation, all females were euthanized and a cesarean section performed. Litters were examined for soft tissue and skeletal alterations. Maternal toxicity was limited to dams receiving TG at 3,870 mg/kg/day. At this dose, body weights and food consumption were reduced during certain periods of gestation. Fetuses derived from those dams exhibited a nonstatistically significant increased incidence of variations when compared to controls. Fetal body weights in the 3,870 mg/kg/day group were significantly lower than controls. There was no increased incidence of anomalies when thiodiglycol-treated fetuses were compared to controls. It was concluded that TG did not produce terata. Developmental toxicity (decreased fetal weights and associated delays in development) occurred only at the maternally toxic dose of 3,870 mg/kg. It appears that 1,290 mg/kg/day could be considered no observed adverse effect level (NOAEL) for oral developmental toxicity. The lowest observed adverse effect level (LOAEL) was 3,870 mg/kg for maternal toxicity.     

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.     

Evaluation of the Developmental Toxicity of Methacrylamide and N,N'-Methylenebisacrylamide in Swiss Mice

Timed-pregnant CD-1 outbred albino Swiss mice received eithermethacrylamlde (MAC; 0, 60, 120, or 180 mg/kg/day) or N,N'-methylenebisacrylamide(BAC; 0, 3, 10, or 30 mg/kg/day) po in distilled water on gestationaldays (GD) 6 through 17. Maternal clinical status was monitoreddaily. At termination (GD 17), confirmed-pregnant females (27–30per group, MAC; 24–25 per group, BAC) were evaluated forclinical status and gestational outcome; live fetuses were examinedfor external, visceral, and skeletal malformations. For MAC,no treatment-related maternal mortality was observed. Maternalbody weight on GD 17, maternal weight gain during treatmentand gestation, and corrected maternal weight gain were reducedat the high dose. Relative maternal food and water intake wasnot adversely affected; neurotoxicity was not observed. Relativematernal liver weight was increased at a 120 mg/kg/day; graviduterine weight was decreased at 180 mg/kg/day. The maternalno-observed adverse effect level (NOAEL) was 60 mg/kg/day. TheNOAEL for developmental toxicity was also 60 mg/kg/day. At 120 mg/kg/day, mean fetal body weight was reduced. At 180 mg/kg/day,increased postimplantation death per litter was observed. Morphologicaldevelopment was not affected. The maternal NOAEL for BAC was10 mg/kg/day. At 30 mg/kg/day, decreased maternal body weighton GD 17, maternal body weight change during treatment and gestation,corrected maternal body weight, and gravid uterine weight wereobserved. Relative maternal liver weight increased at 30 mg/kg/day.The developmental NOAEL was 3 mg/kg/day BAC. Mean fetal bodyweight was reduced at 30 mg/kg/day. At 10 mg/kg/day, an increasedincidence of fetal variations (extra rib) was observed, althoughfetal malformation rate was unaffected. MAC and BAC were notteratogenic to Swiss mice at the doses tested. BAC was morepotent than MAC in causing adverse maternal and developmentaleffects.     

Evaluation of the developmental toxicity of isoeugenol in Sprague-Dawley (CD) rats.

Isoeugenol, used as a perfumery and flavoring agent, was evaluated for developmental toxicity. Timed-pregnant CD((R)) outbred albino Sprague-Dawley rats received isoeugenol (250, 500, or 1000 mg/kg/day) or vehicle (5 ml/kg corn oil) by gavage on gestational days (gd) 6 through 19. Maternal food and water consumption, body weight, and clinical signs were monitored at regular intervals throughout gestation. At termination (gd 20), confirmed-pregnant females (23-25 per group) were evaluated for gestational outcome. All live fetuses were weighed and examined for external malformations, and approximately 50% were evaluated for visceral or skeletal malformations. There were no treatment-related maternal deaths. Clinical signs associated with isoeugenol exposure included dose-related evidence of sedation and aversion to treatment (rooting behavior) in all isoeugenol groups, as well as an increased incidence of piloerection at >/= 500 mg/kg/day. Maternal body weight, weight gain, and gestational weight gain (corrected for gravid uterine weight) were reduced at all doses in a dose-related manner. Gravid uterine weight was significantly decreased at the mid and high doses, whereas maternal relative liver weight was increased at all three dose levels. During treatment (gd 6 to 20), maternal relative food consumption was significantly decreased at the high dose, and maternal relative water consumption was elevated in the mid- and high-dose groups. Prenatal mortality (resorption or late fetal death) was unaffected. At 1000 mg/kg/day, average fetal body weight/litter was decreased by 7% (male) or 9% (female). Incidences of fetal morphological anomalies were statistically equivalent among groups, except for an increase in the incidence of unossified sternebra(e), a skeletal variation, at the high dose. In summary, the maternal toxicity lowest observed adverse effect level (LOAEL) was 250 mg/kg/day based primarily on reduced body weight and gestational weight gain (corrected for gravid uterine weight), and the maternal toxicity no observed adverse effect level (NOAEL) was not determined in this study. The developmental toxicity LOAEL was 1000 mg/kg/day based on intrauterine growth retardation and mildly delayed skeletal ossification. The developmental toxicity NOAEL was 500 mg/kg/day.     

Maternal and developmental toxicity study of sodium azide in rats

Sodium azide (NaN(3)) is being proposed for use as an active ingredient to control a broad spectrum of soil borne pathogens including insects, weeds, nematodes, fungi, and bacteria. The purpose of this study was to determine the maternal and developmental toxicity of NaN(3) in rats. Sperm-positive Sprague-Dawley rats were treated with NaN(3) via oral gavage once daily from Gestation Day (GD) 6 through 19 at respective dose levels of 0, 1, 5, and 17.5mg/kg/day. From GD 10-12, the high-dose was reduced to 10mg/kg/day due to maternal mortality. Cesarean section was performed on GD 20 and implantation and resorptions sites, live and dead fetuses were counted. Fetuses were weighed, sexed externally and processed for gross external, visceral and skeletal examinations. A high rate of maternal mortality; reduced gestation body weight, gestation body weight changes and food consumption; decreased corrected body weight and corrected weight gain were observed at 17.5/10mg/kg/day. Fetal weight was also reduced at 17.5/10mg/kg/day. There were no maternal deaths, clinical signs or body weight effects that were considered related to NaN(3) at 1 and 5mg/kg/day. No increase in the incidence of malformations and variations were observed at any of the doses evaluated. Based on the results of this study, the No Observed Adverse Effect Level (NOAEL) and the Lowest Observed Adverse Effect Level (LOAEL) for maternal and developmental toxicity of NaN(3) in rats were considered to be 5 and 17.5/10mg/kg/day, respectively.     

Developmental toxicity study of Aquacoat ECD ethylcellulose aqueous dispersion administered orally to rats.

A developmental rat toxicity study of Aquacoat((R)) ECD was performed as part of a program to evaluate the safety of the product. Groups of 25 presumed-pregnant Charles River Sprague-Dawley CD rats received doses of 0, 903, 2709 and 4515mg/kg/day (dry weight basis) of Aquacoat ECD administered undiluted once daily via oral gavage on days 6-15 of gestation. All surviving dams underwent caesarean sectioning on day 20 of gestation. Foetuses were weighed, sacrificed and subject to external, visceral and skeletal evaluations. No test material-related maternal deaths occurred; one high-dose female died on day 14 due to gavage error. The only treatment-related clinical sign noted among dams receiving 2709mg/kg/day and greater was pale faeces which was attributed to the presence of the test material in the faeces. No statistically significant differences were noted among the measured maternal parameters. Foetal sex ratios and body weights were similar in all groups. The results of external and visceral foetal evaluations revealed no treatment-related alterations. The only statistically significant findings noted during the skeletal evaluation were increased litter incidences of incompletely ossified or wavy ribs noted among foetuses receiving 4515mg/kg/day, and a significant increase in the litter incidence of thickened ribs at doses of 2709 and 4515mg/kg/day. Given the nature of these findings and the lack of effects on any other parameter measured in this study, they were not considered adverse effects of treatment. Under the conditions of this study, the maternal and foetal no-observed-adverse-effect level (NOAEL) is in excess of 4515mg/mg/day.     

Tetrahydrofuran: two-generation reproduction toxicity in Wistar rats by continuous administration in the drinking water.

In a two-generation reproduction toxicity study, 25 male and 25 female Wistar rats per dose group and generation were exposed continuously to tetrahydrofuran in the drinking water for at least 70 days prior to and during mating, gestation, parturition and lactation to weaning, at concentrations of 0, 1000, 3000 or 9000 ppm (approximately 100, 300 and 700 mg/kg/day in males and females premating, 100, 300 and 800 mg/kg/day in females during gestation, and 200, 500 and 1300 mg/kg/day in females during lactation) through two successive generations. In both generations and sexes, water consumption was dose-relatedly reduced at all doses; food consumption and body weight were reduced at 9000 ppm. Necropsy kidney weights were increased in 9000 ppm F0 males. Pup body weight gain during lactation was reduced in both generations (F1 and F2 pups) and eye opening delayed in the first generation (F1 pups) at 9000 ppm; there were no treatment-related malformations. The NOAEL of tetrahydrofuran in drinking water is 9000 ppm for parental fertility and reproductive performance, and 3000 ppm for systemic parental and developmental toxicity.     

Neonatal mortality from in utero exposure to perfluorooctanesulfonate (PFOS) in Sprague-Dawley rats: dose-response, and biochemical and pharamacokinetic parameters

Perfluorooctanesulfonate (PFOS) is a widely distributed, environmentally persistent acid found at low levels in human, wildlife, and environmental media samples. Neonatal mortality has been observed following PFOS exposure in a two-generation reproduction study in rats and after dosing pregnant rats and mice during gestation. Objectives of the current study were to better define the dose-response curve for neonatal mortality in rat pups born to PFOS-exposed dams and to investigate biochemical and pharmacokinetic parameters potentially related to the etiology of effects observed in neonatal rat pups. In the current study, additional doses of 0.8, 1.0, 1.2, and 2.0 mg/kg/day were included with original doses used in the two-generation study of 0.4 and 1.6 mg/kg/day in order to obtain data in the critical range of the dose-response curve. Biochemical parameters investigated in dams and litters included: (1) serum lipids, glucose, mevalonic acid, and thyroid hormones; (2) milk cholesterol; and (3) liver lipids. Pharmacokinetic parameters investigated included the interrelationship of administered oral dose of PFOS to maternal body burden of PFOS and the transfer of maternal body burden to the fetus in utero and pup during lactation, as these factors may affect neonatal toxicity. Dosing of dams occurred for 6 weeks prior to mating with untreated breeder males, through confirmed mating, gestation, and day four of lactation. Dose levels for the dose-response and etiological investigation were 0.0, 0.4, 0.8, 1.0, 1.2, 1.6, and 2.0 mg/kg/day PFOS. Statistically significant decreases in gestation length were observed in the 0.8 mg/kg and higher dose groups. Decreases in viability through lactation day 5 were observed in the 0.8 mg/kg and higher dose groups, becoming statistically significant in the 1.6 and 2.0 mg/kg dose groups. Reduced neonatal survival did not appear to be the result of reductions in lipids, glucose utilization, or thyroid hormones. The endpoints of gestation length and decreased viability were positively correlated, suggesting that late-stage fetal development may be affected in pups exposed to PFOS in utero and may contribute to the observed mortality. Benchmark dose (BMD) estimates for decreased gestation length, birth weight, pup weight on lactation day 5, pup weight gain through lactation day 5, and viability resulted in values ranging from 0.27 to 0.89mg/kg/day for the lower 95% confidence limit of the BMD5 (BMDL5). Results of analyses for PFOS in biological matrices indicate a linear proportionality of mean serum PFOS concentration to maternal administered dose prior to mating and through the first two trimesters of gestation. However, at 21 days of gestation, mean serum PFOS concentrations were notably reduced from values measured earlier in gestation. Urinary and fecal elimination was low as expected from prior observations in adult rats. Significant transfer of PFOS from dam to fetus in utero was confirmed, and results suggest that dam and corresponding fetal body burdens, as indicated by serum and liver PFOS levels, correlate with neonatal survival.     

Reproductive toxicity studies in rats with rimexolone, a corticoid ophthalmic suspension.

Rimexolone is a potent anti-inflammatory corticosteroid with a lower potential for elevating intraocular pressure, relative to other ophthalmic steroids, and is indicated for postsurgical inflammation and uveitis. Fertility and peri/postnatal toxicities were evaluated at oral gavage doses of 50, 150 or 500 mg/kg, and developmental toxicity at 100, 500, or 1000 mg/kg. In the fertility study, male rats were treated daily beginning 4 weeks prior to mating and females were treated daily beginning 2 weeks prior to mating, and through gestation day 6. Females were necropsied on gestation day 15 and males were necropsied after 10 weeks of exposure. In males, dose-related reductions in mean body weights, body weight gains, and food consumption occurred in all groups. In the 500 mg/kg females, mean body weights were reduced during gestation, and there was an increase in early resorptions and concomitant decrease in viable fetuses at this level. There were no effects on copulation or fertility indices, or on the number of corpora lutea and implantation sites. The no-observed-effect level (NOEL) for fertility and reproductive effects was 150 mg/kg. In the developmental toxicity study, female rats were treated daily from gestation days 6 through 17, necropsied on gestation day 20 and fetuses were evaluated. Maternal toxicity occurred at 500 and 1000 mg/kg as indicated by reduced maternal body weights and body weight gains. However, there was no indication of a developmental effect on fetuses due to rimexolone. The NOEL was 1000 mg/kg for the developing fetuses. In the peri/postnatal toxicity study, female rats were treated daily from gestation day 6 through lactation day 20 and necropsied. F1 developmental and behavioral parameters were evaluated. Selected F1 animals were mated at 12 weeks, allowed to deliver, and necropsied on lactation day 21. At 500 mg/kg, F0 maternal body weights were reduced during gestation and lactation, and F1 pup weights were reduced during lactation and the growth phase. There were no effects on the F1 fertility or reproductive capabilities, or on F2 developmental parameters. The NOEL for the F0 females and F1 offspring was 150 mg/kg. Together, these studies indicate that, unlike some corticosteroids, rimexolone does not produce developmental or reproductive toxicity in rats.     

Maternal and developmental toxicity evaluation of melatonin administered orally to pregnant Sprague-Dawley rats.

Melatonin (MEL) is a widely used, over-the-counter sleep aid, and it has putative contraceptive, antioxidant, antiaging, and anticancer effects. The developmental toxicity potential for repeated oral doses of MEL had not previously been evaluated. In the present studies, time-mated, Sprague-Dawley-derived (CD) rats were administered MEL or vehicle by gavage on gestation days (gd) 6-19. MEL-treated groups received 1-, 10-, 100-, 150-, or 200-mg/kg body weight/day in the screening study (15 rats/group), and 50, 100, or 200 mg/kg/day in the definitive study (25 rats/group). In both studies, maternal food/water consumption, body weight, and clinical signs were monitored at regular intervals throughout gestation. At termination (gd 20, both studies), maternal liver and gravid uterine weights, number of ovarian corpora lutea, conceptus survival, fetal sex, and fetal body weight were evaluated. Fetal morphological examination included external structures (both studies) as well as visceral and skeletal structures (definitive study). In the screening study, maternal serum levels of 17beta-estradiol, progesterone, prolactin, and luteinizing hormone were determined by radioimmunoassay, and mammary tissue was fixed, stained, and evaluated for percent glandular area within the fat pad. No maternal morbidity/mortality was found in either study. In the screening study, aversion to treatment (> or =100 mg/kg/day) and reduced maternal weight gain (> or =150 mg/kg/day) were noted, but reproductive/endocrine parameters and fetal development were not affected. In the definitive study, aversion to treatment was noted at > or =50 mg/kg/day, and mild sedation, reduced maternal food intake, and reduced body weight gain were found during initial treatment with 200 mg/kg/day. MEL had no effect on prenatal survival, fetal body weight, or incidences of fetal malformations/variations. Thus, in the definitive study, the maternal toxicity NOAEL and LOAEL were 100 and 200 mg/kg/day, respectively, and the developmental toxicity NOAEL was > or =200 mg/kg/day.     

Evaluation of the developmental toxicity of formamide in Sprague-Dawley (CD) rats.

Timed-pregnant CD(R) outbred albino Sprague-Dawley rats received formamide (50, 100, or 200 mg/kg/day) or vehicle (5 ml/kg deionized/distilled water, po) on gestational days (gd) 6 through 19. Maternal food and water consumption (absolute and relative), body weight, and clinical signs were monitored at regular intervals throughout gestation. At termination (gd 20), confirmed-pregnant females (21-23 per group) were evaluated for clinical status and gestational outcome; live fetuses were examined for external, visceral, and skeletal malformations and variations. There were no maternal deaths and no dose-related clinical signs. At 200 mg/kg/day, maternal body weight on gd 20, weight gain, and gravid uterine weight were significantly decreased. Maternal weight gain, corrected for gravid uterine weight, liver weight (absolute or relative), and food and water consumption (absolute or relative), were not affected. Formamide did not affect prenatal viability or incidences of fetal malformations or variations. Average fetal body weight/litter was decreased at 100 and 200 mg/kg/day. Fetal body weight was affected at lower daily doses than in previously published studies, possibly due to the longer total exposure period and/or lack of a recovery period between cessation of exposure and termination. In summary, the maternal toxicity no-observed-adverse-effect level (NOAEL) was 100 mg/kg/day and the low observed adverse effect level (LOAEL) was 200 mg/kg/day under the conditions of this study. Similarly, the developmental toxicity NOAEL was 50 mg/kg/day and the LOAEL was 100 mg/kg/day.     

Developmental toxicity evaluation of 1,2,3,4-butanetetracarboxylic acid in Sprague Dawley (CD) rats

1,2,3,4-butanetetracarboxylic acid (BTCA), proposed as a formaldehyde substitute in the treatment of permanent press fabrics, was evaluated for developmental toxicity. Timed-mated CD rats (25 per group) received BTCA 250, 500, or 1000 mg/kg/day or vehicle (deionized/distilled water) by gavage on gestational days (gd) 6 through 19. Maternal feed and water consumption, body weight, and clinical signs were monitored throughout gestation. At termination (gd 20), confirmed-pregnant females (21 to 25 per group) were evaluated for clinical status and gestational outcome; live fetuses were examined for external, visceral, and skeletal malformations. One maternal death, reduced body weight, and reduced weight gain were noted at the high dose; confirmed pregnancy rates were 84 to 100% for each group. There were no treatment-related effects on fetal growth, survival, or morphologic development. The maternal toxicity NOAEL and LOAEL are 500 and 1000 mg/kg/day, respectively. The developmental toxicity NOAEL is > or = 1000 mg/kg/day, and the LOAEL was not established in this study.     

Developmental toxicity of orally administered thiabendazole in ICR mice.

Thiabendazole (TBZ) is a potent anthelmintic and fungicide used in the treatment of parasitic infections in humans and domestic animals and post-harvest protection of agricultural commodities. TBZ is not teratogenic or selectively foetotoxic in rats or rabbits, in contrast to several other benzimidazole derivatives. However, when administered orally to pregnant (Jcl:ICR) mice at lethal dosages, malformations were observed in treated fetuses. To assess whether the effects found in this previous study were attributable to maternal toxicity or TBZ the present study was conducted. TBZ doses of 25, 100 or 200 mg/kg/day were selected based on a preliminary range-finding study in which maternotoxicity was evident at doses of 200 mg/kg/day or above. The compound was administered during gestation days 6-15 as a solution in olive oil. Caesarean sections were completed on gestation day 18 and complete fetal examinations conducted. Decreases in maternal weight gain relative to controls were found at doses of 100 mg/kg/day or above, which paralleled decreases in foetal weights in these same dose groups. However, there were no treatment-related external, visceral or skeletal anomalies in any treatment group. Therefore, TBZ was not teratogenic or selectively foetotoxic in mice, with no-observed-effect levels (NOEL) of 25 and greater than 200 mg/kg/day for maternal and fetal weight effects and teratogenicity, respectively. These results indicate that foetal effects noted in previous studies in mice were probably secondary to severe maternal toxicity.     

Evaluation of the developmental toxicity of leucomalachite green administered orally to rats

Malachite green (MG) had been extensively used worldwide in the past few decades as an effective fungicide, bactericide, ectoparasiticide, and antiprotozoan on fish. It is rapidly and extensively metabolized to leucomalachite green (LMG) in fishes.To study the developmental toxicity of LMG, we evaluated the maternal and embryo/fetal effects of LMG orally administered to Sprague–Dawley rats once daily from day 6–15 of gestation at dose levels of 0, 10, 80, and 160 mg/kg/day. In the current investigation, the unmetabolized compound (LMG) was detected in the plasma of the dams treated with LMG and in the amniotic fluid. At dose levels of 80 and 160 mg/kg/day, LMG induced maternal toxicity, which consisted of severe reduction in maternal weight and food consumption during the treatment period. Doses of 80 and 160 mg/kg/day induced fetal skeletal abnormalities. The major skeletal defects were bipartite ossification of the thoracic centrum. LMG at 160 mg/kg/day also induced marked embryolethality and visceral abnormalities. Based on the results of this study, a dose level of 10 mg/kg/day is considered the no-observed-adverse-effect-level (NOAEL) for maternal and fetal developmental toxicity in rats.