Developmental toxicity evaluation of sodium fluoride administered to rats and rabbits in drinking water.

Sodium fluoride (NaF; Cas No. 7681-49-4) is used in fluoridating municipal water supplies, resulting in chronic exposure of millions of people worldwide. Because of a lack of pertinent developmental toxicity studies in the literature, sodium fluoride was administered ad libitum in deionized/filtered drinking water (to mimic human exposure) to Sprague-Dawley-derived rats (26/group) on Gestation Days (GD) 6 through 15 at levels of 0, 50, 150, or 300 ppm and New Zealand White rabbits (26/group) on GD 6 through 19 at levels of 0, 100, 200, or 400 ppm. Higher concentrations via drinking water were not practicable due to the poor palatability of sodium fluoride. Drinking water (vehicle) contained less than 0.6 ppm sodium fluoride (limit of detection) and sodium fluoride content of the feed was 12.4 ppm fluoride (rats) and 15.6 ppm fluoride (rabbits). Maternal food, water, body weights, and clinical signs were recorded at regular intervals throughout these studies. Animals were killed on GD 20 (rats) or 30 (rabbits) and examined for implant status, fetal weight, sex, and morphological development. In the high-dose group of both studies there was an initial decreased maternal body weight gain which recovered over time and a decreased water consumption--attributed to decreased palatability. No clear clinical signs of toxicity were observed. Maternal exposure to sodium fluoride during organogenesis did not significantly affect the frequency of postimplantation loss, mean fetal body weight/litter, or external, visceral or skeletal malformations in either the rat or the rabbit. The NOAEL for maternal toxicity was 150 ppm sodium fluoride in drinking water (approximately 18 mg/kg/day) for rats, and 200 ppm (approximately 18/mg/kg/day rabbits. The NOAEL for developmental toxicity was > or = 300 ppm sodium fluoride (approximately 27 mg/kg/day) for rats and > or = 400 ppm (approximately 29 mg/kg/day) for rabbits administered during organogenesis in drinking water. The total exposure to fluoride (mg F/kg body weight/day from food and drinking water combined) in the mid- and high-dose groups for both species was > 100-fold higher than the range at 0.014-0.08 mg F/kg/day estimated for a 70-kg person from food and fluoridated (1 ppm) drinking water.

Developmental toxicity of sarin in rats and rabbits.

Sarin (Agent GB, isopropyl methylphosphonofluoridate) is an organophosphate cholinesterase inhibitor. Sarin (Type I or Type II) was administered by gavage to CD rats on d 6-15 of gestation at dose levels of 0, 100, 240, or 380 micrograms/kg/d and to New Zealand White (NZW) rabbits on d 6-19 of gestation at dose levels of 0, 5, 10, or 15 micrograms/kg/d. Females were weighed on gestational days (GD) 0, 6-16 for rats and 6-20 for rabbits, and immediately prior to termination (GD 20 for rats and GD 29 for rabbits). All animals were monitored daily for clinical signs of toxicity throughout dosing and until sacrifice. At necropsy, gravid uteri were weighed and examined for the number and status of implants (live, resorbed, or dead). Individual fetal body weight, malformations, and variations (external, visceral, and skeletal) were recorded. Rat and rabbit dams in the high-dose groups exhibited significant signs of maternal toxicity and increased maternal mortality. Examination of gravid uteri revealed no statistical differences among treatment groups in the incidence of resorptions or of dead or malformed fetuses, or in average body weight of live fetuses per litter. These results show no evidence or developmental toxicity in the CD rat or NZW rabbit following exposure to either Type I or Type II sarin during embryonic differentiation and major organogenesis, even at a dose that produced maternal toxicity.

Behavioral teratology and dominant lethal evaluation of nitrous oxide exposure in rats.

Epidemiological studies have suggested that spontaneous abortion may be increased in medical personnel following the sort of chronic low-level exposure to the anesthetic gas nitrous oxide (N2O) seen in surgical or dental operatories. These results are supported by some, but not all, animal studies, and results are less well established at low exposure levels. Behavioral effects in exposed animal offspring have also been observed, but again not in all studies. To further examine this problem, we conducted the present experiments. Adult male or female rats were exposed to trace concentrations of N2O (0%, 0.1%, 0.5%, or 1.0% in air) for 6 h daily either throughout gestation (females) or for 9 weeks (males). Offspring from treated adults were subjected to an extensive behavioral test battery. There were no clear dose-response effects on any of eight behavioural tests for any offspring. Maternal and offspring weights were normal from conception through adulthood. Additionally, we studied effects of N2O on male fertility by mating treated males with untreated females and examining uterine contents. There was no evidence for a substantial decline in fertility of exposed males, although there was a small dose-related trend for resorptions to increase and live births to decrease with increasing paternal N2O exposure. There results suggest that there is little alteration in male or female fertility following chronic exposure to low levels of N2O. There are also no significant long-term behavioral alterations in offspring exposed gestationally to trace levels of N2O via dam or sire.

Developmental neurotoxicity evaluation of orally administered isopropanol in rats.

Isopropanol was administered by gavage to timed-mated rats from Gestation Day (GD) 6 through Postnatal Day (PND) 21. Doses administered were 0, 200, 700, or 1200 mg/kg/day in a volume of 5 ml/kg. The dams were allowed to deliver and body weights and food consumption were recorded during gestation and lactation. Pups were counted, examined, sexed, and weighed on PND 0, 4, 7, 13, 17, 21, 36, 49, and 68. Litters were culled to eight pups (4:4 or 5:3 sex ratio) on PND 4 and litters without acceptable numbers of male and female pups were eliminated from the study. Pups were weaned on PND 22, and two pups from each litter and their dams were killed. Six of these pups from each dose group were perfused in situ for histopathological examination of the central and peripheral nervous system. Brains of the remaining pups were divided into four regions and weighed. Maternal liver and kidney weights were recorded. Weaned pups were assessed for day of testes descent or vaginal opening and for motor activity on PNDs 13, 17, 21, 47, and 58; auditory startle on PNDs 22 and 60; and active avoidance on PNDs 60-64. These pups were euthanized and examined on PND 68. One high-dose dam died on PND 15, but there were no other clinical observations or effects on maternal weight, food consumption, or gestation length. Pup survival, weight, sex ratio, and sexual maturation were unaffected. There were no biologically significant findings in the behavioral tests, no changes in organ weights, and no pathological findings that could be attributed to isopropanol exposure. In conclusion, there was no evidence of developmental neurotoxicity associated with isopropanol exposure as high as 1200 mg/kg/day.

Effects of reproductive tract glutathione enhancement and depletion on ethyl methanesulfonate-induced dominant lethal mutations in Sprague-Dawley rats.

The effects of altering glutathione (GSH) levels in the male reproductive tract have been studied in an attempt to establish a link between chemical-induced perturbations in glutathione and susceptibility of spermatozoa to chemical insult. Tissue GSH levels were enhanced by a treatment regimen of N-acetylcysteine (NAC) (250 mg/kg, 4 treatments at 2 h intervals). With this treatment, GSH levels in liver, testis, caput epididymis, and cauda epididymis were elevated to 126%, 110%, 178%, and 136% of control values. Sexually mature male rats were then treated with NAC and challenged with a dose of EMS (100 mg/kg) to determine if enhanced tissue GSH would protect against EMS-induced dominant lethal mutations. Pretreatment with NAC significantly decreased the post-implantation loss from 7.05 +/- 0.57 with EMS alone to 5.28 +/- 0.47. Conversely, a dominant lethal assay was conducted using different doses of phorone pretreatment to determine the relative contribution of hepatic versus reproductive tract GSH in protecting against EMS-induced dominant lethal resorptions. Doses of 100 mg/kg and 250 mg/kg phorone significantly lowered both hepatic and reproductive tract GSH while 25 mg/kg lowered only hepatic GSH. These three dose levels were used as pretreatments in a dominant lethal study followed by a challenge administration of EMS (50 mg/kg), which is a threshold dose of EMS for producing dominant lethal mutations. Comparison against controls demonstrated a significant potentiation of fetal resorptions in all groups receiving phorone pretreatment, including the 25 mg/kg pretreatment group which only lowered hepatic GSH prior to EMS challenge. The results of these experiments indicate that GSH reserves in the male reproductive tract are insufficient to protect developing spermatozoa from damage by alkylating agents in the absence of hepatic GSH.

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.

Effects of selected chemicals on the glutathione status in the male reproductive system of rats.

Previous studies have suggested a significant role for reproductive tract glutathione in protecting against chemical-induced germ-cell mutations. Therefore, a number of compounds were tested for their ability to perturb glutathione levels in the testes and epididymides as well as liver following single acute dosages to rats. Phorone (250 mg/kg), isophorone (500 mg/kg), and diethyl maleate (500 mg/kg) significantly reduced glutathione in the liver and in both reproductive organs examined. Methyl iodide (100 mg/kg), trimethyl phosphate (600 mg/kg), naphthalene (500 mg/kg), acetaminophen (1500 mg/kg), and pentachlorophenol (25 mg/kg) affected hepatic and epididymal glutathione, but had little or no effect on testicular levels. The ability of isophorone to enhance the covalent binding of tritiated ethyl methanesulfonate (3H-EMS) to spermatocytes was assessed. Perturbation of reproductive tract glutathione by isophorone treatment significantly enhanced the extent of 3H-EMS-induced binding to sperm heads. The temporal pattern of ethylations in sperm heads was consistent with the stage of sperm development known to be susceptible to ethylations by EMS. Therefore, chemical-induced lowering of glutathione in the male reproductive tract may be a mechanism for potentiation of chemical-induced germ-cell mutations.

Developmental exposure of mice to pulsed ultrasound.

Exposure of pregnant mice on gestation day (gd) 8 to 1 MHz continuous-wave ultrasound (0, 0.05, 0.50, or 1.00 W/cm2) was reported previously to result in a slight (nonsignificant) increase in malformations. The present study was conducted in a similar fashion using pulsed ultrasound but was designed to maximize the likelihood of finding effects of gd 8 ultrasound exposure on prenatal development. Pregnant ICR mice (approximately 60 animals/group) were exposed on gd 8 to pulsed ultrasound with a center frequency of 1 MHz at levels of 0 (sham control), 0.05, 0.50, or 1.00 W/cm2 (spatial average, temporal average intensities; ISATA) with a spatial peak, pulse average intensity (ISPPA) of 90 W/cm2 and pulse duration of 6.5 microseconds. Anesthetized animals were placed in a degassed water bath (30 degrees C) and exposed for two 10 min intervals during which the beam was centered 1 cm on either side of the abdominal midline. On gd 17, dams were killed; the uterus and its contents were weighed and examined; and live fetuses were weighed and examined for external, visceral, and skeletal malformations. Although one female in the 0.50 W/cm2 group and seven animals in the 1.00 W/cm2 group died following exposure, no other significant change from controls was seen in any maternal or fetal parameter evaluated. Thus the results of this study indicate that there was no detectable effect on prenatal development of mice following exposure to ultrasound on gd 8 (a time of maximal sensitivity), even at exposure intensities that were lethal to some maternal animals.