Variability in the developmental toxicity of bropirimine with the day of administration

The aim of this study was to determine the mechanism by which bropirimine exerts its developmental toxicity. This drug is an immunomodulator and interferon inducer with antiviral and antitumor activities in experimental models. Timed-pregnant Upj:TUC(SD)spf (Sprague-Dawley) rats were given a single oral (gastric intubation) dose of bropirimine at 200 or 400 mg/kg (doses as high as 100 mg/kg/day have been employed in human cancer trials) on days 5, 6, 7, 8, 9, 10, 11, or 12 of gestation and in a second experiment on day 12, 13, 14, 15, 16, 17, 18, or 19 of gestation. The dams were killed 24 hours after dosing and their uterine contents examined. In a third experiment, bropirimine (400 mg/kg) was administered on day 4 of gestation and the uteri of different groups were examined on day 8, 9, 10, 11, or 12 of gestation. Serum progesterone levels were measured at sacrifice. In the first two experiments a battery of hematologic/clinical chemistry assays also were performed. In all three experiments, bropirimine-related maternal toxicity was observed; such toxicity was characterized by significant decreases in weight gain, relative to the concurrent vehicle controls, as well as significant differences in several blood parameters including platelets, white blood cells, alanine aminotransferase, and aspartate transaminase. In the first experiment, bropirimine treatment on day 11, but not day 12, resulted in significant decreases in the mean number of live embryos per litter. In the second experiment, significant decreases in the number of live fetuses per litter occurred 24 hours after dosing on day 18 (200 and 400 mg/kg groups) or day 19 (400 mg/kg group). Decreases in serum progesterone appeared to correlate well with the embryolethal effects seen after treatment between days 6 and 11 of gestation, but not with the fetal lethality seen when treatment was given on day 17 or 18. The decreases in serum progesterone levels found most likely were the result of a luteolytic effect, although it is unknown if bropirimine has a direct or indirect effect on the corpora lutea. In the third experiment, bropirimine treatment on day 4 of gestation resulted in only slight preimplantational losses, but significant decreases were found in mean number of live embryos per litter after day 9. Uterine decidual necrosis has been observed in the first experiment where bropirimine was given on day 11; however, treatment on day 4 resulted in an apparent decrease in decidual development but not necrosis.     

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.     

Prevention of tilorone developmental toxicity with progesterone.

The immunomodulator tilorone hydrochloride was administered (gastric intubation) once to time-pregnant Upj:TUC(SD)spf (Sprague-Dawley) rats in four experiments. In experiment 1, tilorone (250 or 500 mg/kg) was administered on day 10 of gestation. The dams were killed 4 or 72 hr after dosing. Interferon-like activity and drug levels were determined in maternal blood, spleen, and thymus, as well as in the embryos. In experiment 2, the test groups received progesterone (2 mg/kg), or tilorone (200 or 400 mg/kg), or progesterone and tilorone. The dams from each group were killed 24 or 48 hr after receiving tilorone. Experiment 3 was similar to experiment 2, except that the dams were killed on gestation day 20. In experiment 4, tilorone (400 mg/kg) was administered on gestation day 17, 18, or 19, and the dams were killed 24 hr after dosing or on gestation day 20. In all four experiments, tilorone-related maternal toxicity (regardless of whether progesterone also was administered) was observed, as characterized by marked decreases in weight gain, the occurrence of clinical signs, and in experiment 1 by decreased thymus weights, 72 hr post-dosing. Dose-related increases in the mean number of dead embryos and in serum interferon titers occurred 72 hr postdosing. In experiment 2, there was an increase in the number of dams in the 400-mg/kg (tilorone only) group with dead embryos only, 24 hr postdosing; similar results occurred in both the 200- and 400-mg/kg groups, 48 hr postdosing. However, in the groups that also received progesterone, a partial prevention of such embryolethality was evident. In experiment 3, embryotoxicity again was observed in both tilorone-treated groups, whereas several of the dams that were also given progesterone through day 19 of gestation experienced at least a partial prevention of the embryolethal effects of tilorone. In experiment 4, no fetotoxicity was observed despite the severe maternal toxicity evident.     

Developmental toxicity of carbon black oil in mice

BACKGROUND: Carbon black oil (CBO) is a refinery side-stream product used to produce asphalt and other commercial products. CBO contains several classes of hydrocarbons, several of which are known to exhibit systemic and gestational toxicities, making this mixture a candidate for causing reproductive toxicity. METHODS: Swiss-Webster mice were administered CBO (300, 350, 400 mg/kg/day) via oral gavage in a dosage volume of 10 microl/g body weight on gestation days (GD) 6-15. Uterine contents were evaluated on GD 18. RESULTS: Treatment with CBO at all dosage levels resulted in a high frequency of maternal clinical symptoms and a decrease in maternal weight gain. Decreased fetal viability was observed, manifested as a decrease in viable implants and, in a high percentage of treated dams, as early resorption of the entire litter. A significant reduction in fetal weight was also observed. However, neither structural malformations nor developmental delays in ossification were observed in any of the living offspring. To minimize maternal toxicity, the dosage range was lowered (100, 200, 300 mg/kg/day), and the concentration was adjusted such that the volume administered to each dam was decreased by 20%. In this trial, the only maternal effect observed was an increase in maternal liver weight at 200 and 300 mg/kg. The fetal lethality effects observed previously were reduced substantially. Nevertheless, the frequency of resorption among all treatment groups was higher statistically than in controls. CONCLUSIONS: These data support the hypothesis that CBO is reproductively toxic in Swiss-Webster mice at oral doses of >/=100 mg/kg/day.     

Dose–Response Effects of Diphenylhydantoin on Pregnant Dams and Embryo‐Fetal Development in Rats

Despite the widespread use of diphenylhydantoin (DPH), there is a lack of reliable information on the teratogenic effects, correlation with maternal and developmental toxicity, and dose–response relationship of DPH. This study investigated the dose–response effects of DPH on pregnant dams and embryo‐fetal development as well as the relationship between maternal and developmental toxicity. DPHwas orally administered to pregnant rats from gestational days 6 through 15 at 0, 50, 150, and 300 mg/kg/day. At 300 mg/kg, maternal toxicity including increased clinical signs, suppressed body weight, decreased food intake, and increased weights of adrenal glands, liver, kidneys, and brain were observed in dams. Developmental toxicity, including a decrease in fetal and placental weights, increased incidence of morphological alterations, and a delay in fetal ossification delay also occurred. At 150 mg/kg, maternal toxicity manifested as an increased incidence of clinical signs, reduced body weight gain and food intake, and increased weights of adrenal glands and brain. Only minimal developmental toxicity, including decreased placental weight and an increased incidence of visceral and skeletal variations, was observed. No treatment‐related maternal or developmental effects were observed at 50 mg/kg. These results show that DPH is minimally embryotoxic at a minimal maternotoxic dose (150 mg/kg/day) but is embryotoxic and teratogenic at an overt maternotoxic dose (300 mg/kg/day). Under these experimental conditions, the no‐observed‐adverse‐effect level of DPH for pregnant dams and embryo‐fetal development is considered to be 50 mg/kg/day. These data indicate that DPH is not a selective developmental toxicant in the rat.     

Effects of tert-butyl acetate on maternal toxicity and embryo-fetal development in Sprague-Dawley rats

This study investigated the potential adverse effects of tert-butyl acetate (TBAc) on maternal toxicity and embryo-fetal development after maternal exposure of pregnant rats from gestational days 6 through 19. TBAc was administered to pregnant rats by gavage at 0, 400, 800, and 1,600 mg/kg/day. All dams were subjected to a Caesarean section on day 20 of gestation, and their fetuses were examined for any morphological abnormalities. At 1,600 mg/kg, maternal toxicity manifested as increases in the incidence of clinical signs and death, lower body weight gain and food intake, increases in the weights of adrenal glands and liver, and a decrease in thymus weight. Developmental toxicity included a decrease in fetal weight, an increase in the incidence of skeletal variation, and a delay in fetal ossification. At 800 mg/kg, only a minimal developmental toxicity, including an increase in the incidence of skeletal variation and a delay in fetal ossification, were observed. In contrast, no adverse maternal or developmental effects were observed at 400 mg/kg. These results show that a 14-day repeated oral dose of TBAc is embryotoxic at a maternally toxic dose (i.e., 1,600 mg/kg/day) and is minimally embryotoxic at a nonmaternally toxic dose (i.e., 800 mg/kg/day) in rats. However, no evidence for the teratogenicity of TBAc was noted in rats. It is concluded that the developmental findings observed in the present study are secondary effects to maternal toxicity. Under these experimental conditions, the no-observed-adverse-effect level of TBAc is considered to be 800 mg/kg/day for dams and 400 mg/kg/day for embryo-fetal development.     

Monomethylarsonic acid and dimethylarsinic acid: developmental toxicity studies with risk assessment

BACKGROUND: The toxicity of arsenic compounds is highly dependent on the valence and methylation state of the compound. Although there is extensive published literature on the potential developmental toxicity of inorganic arsenic compounds, little exists on organic arsenic compounds and, in particular, studies conducted in accordance with conventional regulatory guidelines appropriate for risk assessment are rare. The organic arsenic compounds, monomethylarsonic acid (MMAV) and dimethylarsinic acid (DMAV, also called cacodylic acid), are the active ingredients in pesticide products that are used mainly for weed control. MMAV and DMAV are also metabolites of inorganic arsenic formed intracellularly by most living organisms (animals, plants and bacteria). In mammals, this occurs predominantly in liver cells. METHODS: Conventional developmental toxicity studies of orally administered MMAV and DMAV in the Sprague-Dawley rat and New Zealand White rabbit were conducted in commercial contract laboratories in the late 1980 s for regulatory compliance. The results of these studies are summarized and presented to broaden the data available in the public domain. RESULTS: In both species, data shows an absence of dose-related effects at organic arsenic exposures that were not maternally toxic. MMAV doses of 0, 10, 100, and 500 mg/kg/day (rat) and 0, 1, 3, 7, and 12 mg/kg/day (rabbit) and DMAV doses of 0, 4, 12, and 36 mg/kg/day (rat) and 0, 3, 12, and 48 mg/kg/day (rabbit) were administered by oral gavage daily during organogenesis (Gestation Day [GD] 6-15, rat; GD 7-19, rabbit) and the litters examined at maternal sacrifice (GD 20, rat; GD 29, rabbit). After treatment with MMAV, maternal and fetal toxicity were observed at the highest doses of 500 mg/kg/day (rat) and 12 mg/kg/day (rabbit), but no treatment-related developmental toxicity at the lower doses, even in the presence of minimal maternal toxicity in the rat at 100 mg/kg/d. There was no evidence of teratogenicity associated with MMAV treatment. With DMAV, maternal and developmental toxicity were observed in the rat at 36 mg/kg/day, with a higher than spontaneous incidence of fetuses with diaphragmatic hernia. In the rabbit at 48 mg/kg/day, there was marked maternal toxicity, culminating for most females in abortion and with no surviving fetuses for evaluation. There was no treatment-related maternal or developmental toxicity in the rat or rabbit at 12 mg/kg/day. Based on pregnancy outcome, the developmental toxicity no observed adverse effect level (NOAEL) for orally administered MMAV were 100 and 7 mg/kg/day in the rat and rabbit, respectively, and for DMAV were 12 mg/kg/day in both species. CONCLUSIONS: Margins of exposure estimated based on conservative estimates of daily intakes of arsenic in all of its forms indicate that exposure to MMAV or DMAV at environmentally relevant exposure levels, by the oral route (the environmentally relevant route of exposure) is unlikely to pose a risk to pregnant women and their offspring.     

Developmental toxicity of dichloroacetate in the rat.

Dichloroacetic acid (DCA) is a principal by-product of the chlorine disinfection of water containing humic and fulvic acids, and is also a drug of interest in the therapeutic management of metabolic disorders. The developmental effects of DCA were evaluated in the pregnant Long-Evans rat. In two separate studies, animals were dosed by oral intubation on gestation days 6-15 (plug = 0) with 0, 900, 1,400, 1,900 or 2,400 mg/kg/day and 0, 14, 140, or 400 mg/kg/day. The vehicle control was distilled water. Maternal observations included clinical signs, weight change, and gross evaluation of organ weights and uterine contents at necropsy (day 20). Corpora lutea were counted and uteri stained for implantation sites. Live fetuses were examined for external, skeletal, and soft tissue malformations. Seven dams died during treatment (1,400 mg 1/19, 1,900 mg 2/19, 2,400 mg 4/21), and maternal weight gain was reduced at all except the lowest treatment levels. Liver, spleen, and kidney weights increased in a dose-related manner. The mean percentage of resorbed implants per litter was significantly elevated at greater than or equal to 900 mg/kg/day. Live fetuses showed dose-dependent reductions in weight and length at doses above 140 mg/kg. Statistically significant frequencies of soft tissue malformations ranged from 2.6% (140 mg/kg) to 73% (2,400 mg/kg). These were principally in the cardiovascular system and predominantly comprised defects between the ascending aorta and the right ventricle. Skeletal malformations were not observed in significant numbers in any dose group.(ABSTRACT TRUNCATED AT 250 WORDS)     

Developmental toxicity evaluation of orthovanadate in the mouse

Sodium orthovanadate in deionized water was administered once daily by gavage on gestational days 6-15 to mice at doses of 0, 7.5, 15, 30, and 60 mg/kg. Dams were killed on day 18 of pregnancy, and fetuses were examined for external, visceral, and skeletal defects. Maternal toxicity was observed at the highest doses of sodium orthovanadate, as evidenced by a significant number of deaths (60 and 30 mg/kg/d) and reduced weight gain and food consumption (30 and 15 mg/kg/d). Embryolethality and teratogenicity were not observed at maternally toxic doses and below, but fetal toxicity was evidenced by a significant delay in the ossification process of some skeletal districts at 30 mg/kg/d. The no-observed-adverse-effect level (NOAEL) for maternal toxicity was 7.5 mg/kg/d, and 15 mg/kg/d represented a NOAEL for developmental toxicity in mice under the conditions of this study.     

Postnatal development of rat pups after maternal exposure to diethanolamine

BACKGROUND: Diethanolamine (DEA), a widely used surfactant, was administered to pregnant mice at the oral LD10 resulting in failure of pups to grow and thrive through postnatal day (PND) 3 [National Toxicology Program, 1987; York et al., Teratology 37:503-504, 1988]. The toxicity profile for DEA differs among rodent species. This study investigated DEA-induced postnatal toxicity in a second species. METHODS: Timed-mated Sprague-Dawley rats were dosed (0, 50, 125, 200, 250, or 300 mg DEA/kg/day, p.o.) on gestational days (GD) 6-19. Dams and pups were monitored for body weight, feed/water intake, clinical signs, litter size, and sex ratio. At necropsy (PND 21), maternal liver and kidney weights and number of uterine implantation sites were recorded. RESULTS: The high-dose group was terminated early due to excessive toxicity. The estimated maternal LD10 was 218 mg/kg/day. Maternal effects included decreased body weight and relative feed intake (>or=200 mg/kg/day), transiently reduced relative water intake (125 and 250 mg/kg/day), and increased absolute kidney weight (>or=125 mg/kg/day). Postimplantation loss (PND 0) and pup mortality (PND 0-4) were increased (>or=200 and >or=125 mg/kg/day, respectively). Pup body weight was reduced (>or=200 mg/kg/day) as late as PND 21. CONCLUSIONS: This study demonstrates reduced postnatal growth and survival in a second species after gestational exposure to DEA, persistence of toxic effects through the end of lactation, possibly due to long elimination half-life, and maternal and developmental toxicity no-observed-adverse-effect level (NOAELs) (50 mg/kg/day) and lowest-observed-adverse-effect level (LOAELs) (125 mg/kg/day) for oral DEA exposure during embryo/fetal development in the rat.     

Embryotoxicity and teratogenicity of uranium in mice following subcutaneous administration of uranyl acetate

The effects of multiple maternal subcutaneous injections of uranyl acetate dihydrate (0.5, 1, and 2 mg/kg/d) from d 6 to d 15 of gestation were evaluated in Swiss mice. External, internal soft-tissue and skeletal examinations of fetuses were performed on gestation d 18. Maternal toxicity occurred in all uranium-treated groups as evidenced primarily by deaths as well as significant decreases in weight gain and in body weight at termination. Although it was not dose-related, embryotoxicity also occurred in all uranium-treated groups (significant increases in the number of nonviable implantations and in the percentage of postimplantation loss). Fetal body weight was significantly decreased at 1 and 2 mg/kg/d, whereas the number of total internal and total skeletal defects showed dose-dependent increases at 0.5, 1, and 2 mg/kg/d. Most morphological defects were developmental variations, whereas malformations were only detected at 1 and 2 mg/kg/d. On the basis of these data, both the maternal no-observable-adverse-effect level (NOAEL) and the NOAEL for embryotoxicity of uranyl acetate dihydrate were below 0.5 mg/kg/d, whereas the NOAEL for teratogenicity was 0.5 mg/kg/d.     

Maternal and developmental toxicity of low doses of cytosine arabinoside in mice

1-beta-D-Arabinofuranosylcytosine (Ara-C), an effective drug for the treatment of leukemia and breast cancer, was evaluated for developmental toxicity in pregnant Swiss mice. Ara-C was administered by intraperitoneal injection on gestational days 6-15 at doses of 0, 0.5, 2, and 8 mg/kg/day. Maternal observations included clinical signs, body weight change, food consumption, and gross evaluation of organs and uterine contents at necropsy (day 18). Live fetuses were examined for external, visceral, and skeletal alterations. Maternal toxicity was observed at 2 and 8 mg/kg/day, as evidenced by a significant decrease in body weight gain and food consumption during the treatment period. Significantly increased early and late resorptions and reduced number of live fetuses per liter as well as decreased fetal body weight were observed at 8 mg/kg/day. At 2 mg/kg/day, the incidence of cleft palate, renoureteral agenesis or hypoplasia, and poly- or oligodactyly was significantly increased, whereas fetal weight was reduced at 0.5 mg/kg/day. Thus, the developmental no-observed-adverse-effect-level (NOAEL) of Ara-C in the pregnant mouse is lower than 0.5 mg/kg/day, while the NOAEL for maternal toxicity is 0.5 mg/kg/day. We believe that exposure to this agent ought to be avoided during organogenesis.     

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 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.     

Evaluation of the protective activity of deferiprone, an aluminum chelator, on aluminum-induced developmental toxicity in mice

BACKGROUND: Since deferiprone can be an effective chelating agent for the treatment of aluminum (Al) overload, in the present study we investigated whether this chelator could protect against Al-induced maternal and developmental toxicity in mice. METHODS: A single oral dose of Al nitrate nonahydrate (1,327 mg/kg) was given on gestation day 12, the most sensitive time for Al-induced maternal and developmental toxic effects in mice. At 2, 24, 48, and 72 hr thereafter, deferiprone was given by gavage at 0 and 24 mg/kg. Cesarean sections were performed on day 18 of gestation and fetuses were examined for malformations and variations. RESULTS: Aluminum-induced maternal toxicity was evidenced by significant reductions in body weight gain, corrected body weight change, and food consumption. Developmental toxicity was evidenced by a significant decrease in fetal weight per litter and an increase in the total number of fetuses and litters showing bone retardation. No beneficial effects of deferiprone on these adverse effects could be observed. By contrast, a more pronounced decrease in maternal weight gain and corrected body weight change, as well as a higher number of litters with fetuses showing skeletal variations was noted in the group exposed to Al nitrate and treated with deferiprone at 24 mg/kg. CONCLUSIONS: According to the current results, deferiprone would not be effective to prevent Al-induced maternal and embryo/fetal toxicity in mice.     

Evaluation of developmental toxicity induced by anticholinesterase insecticide,diazinon in female rats

Developmental toxicities, including birth defects, are significant public health problems. This study was planned to assess the cholinergic and developmental potentials of diazinon that is widely used as an organophosphate insecticide. Pregnant female Sprague‐Dawley rats were given diazinon orally at doses of 0, 1.9, 3.8, and 7.6 mg/kg body weight (b.w.)/day on gestation days 6 to 15. Maternal brain acetylcholinesterase activities, measured on gestation day20, were significantly decreased at 3.8 and 7.6 mg/kg b.w./day, but fetal acetylcholinesterase activity was not altered. Maternal toxicities, as evidenced by cholinergic symptoms including diarrhea, tremors, weakness, salivation, and decreased activities, were observed at the 3.8 and 7.6 mg/kg b.w./day dose groups. Net gravid uterine weight was decreased at a dose of 7.6 mg/kg b.w./day. No maternal effects were apparent in the 1.9 mg/kg b.w./day dose group. Maternal toxicity at a dose of 3.8 mg/kg b.w./day did not induce fetotoxicity or teratogeneicity. However, 7.6 mg/kg b.w./day doses significantly resulted in fetal toxicity and malformations in addition to maternal toxicity in animals. In conclusion, teratogenic disorders only outlined by doses that produced marked maternal toxicity. Since the malformations were not morphologically related, they were considered to be secondary to maternal toxicity; hence, the malformations were not related to cholinesterase inhibition. Birth Defects Res (Part B) 92:534–542, 2011. © 2011 Wiley Periodicals, Inc.     

Evaluation of developmental toxicity in rats exposed to the environmental estrogen bisphenol A during pregnancy.

Bisphenol A (BPA) is an essential component of epoxy resins used in the lacquer lining of metal food cans, as a component of polycarbonates, and in dental sealants. The present study was conducted in an attempt to evaluate the adverse effects of the environmental estrogen BPA on initiation and maintenance of pregnancy and embryofetal development after maternal exposure during the entire period of pregnancy in Sprague-Dawley rats. The test chemical was administered by gavage to mated females from days 1 to 20 of gestation (sperm in varginal lavage = day 0) at dose levels of 0, 100, 300, and 1000 mg/kg. All females were subjected to caesarean section on day 21 of gestation and their fetuses were examined for external, visceral and skeletal abnormalities. In the 1000 mg/kg group, significant toxic effects including abnormal clinical signs, decreased maternal body weight and body weight gain, and reduced food consumption were observed in pregnant rats. An increase in pregnancy failure was also found in the successfully mated females. In addition, increased number of embryonal deaths, increased postimplantation loss, reduced litter size and fetal body weight, and decreased number of fetal ossification centers of several skeletal districts were seen. On the contrary, no significant changes induced by BPA were detected in the number of corpora lutea and implantation sites and by fetal morphological examinations. In the 300 mg/kg group, suppressed maternal body weight and body weight gain, decreased food intake and reduced body weight of male fetuses were seen. There were no adverse signs of either maternal toxicity or developmental toxicity in the 100 mg/kg group. It was concluded that BPA administration during the entire period of pregnancy in rats produced pregnancy failure, pre- and postimplantation loss, fetal developmental delay and severe maternal toxicity, but no embryo-fetal dysmorphogenesis at an oral exposure level of 1000 mg/kg.     

Embryotoxicity of oral administered chlorothalonil in mice

BACKGROUND: Chlorothalonil (2,4,5,6-tetrachloroisophthalonitril), the nephrotoxic fungicide, was examined for its potential to produce developmental toxicity in mice after oral administration. METHODS: Pregnant ICR (CD-1) mice were given sublethal doses of 0 (corn oil), 100, 400, and 600 mg/kg/day chlorothalonil by gavage on gestation days (GD) 6-15. RESULTS: Maternal effects in 400 and 600 mg/kg/day dose groups included signs of toxicity such as weakness and depression in the maternal activity, and reduction in body weight and weight gain. No maternal toxicity was apparent in the 100 mg/kg/day dose group. Maternal exposure to chlorothalonil during organogenesis significantly affected the number of live fetuses, early resorption, and mean fetal weight in the 400 and 600 mg/kg/day dose groups. No external, visceral, and skeletal abnormalities were observed among any of the treated groups compared to the control. CONCLUSIONS: On the basis of the present results chlorothalonil can produce clinical signs of toxicity and fetotoxicity without teratogenic effects at 400 and 600 mg/kg/day dose groups.     

Teratogenic and postnatal developmental studies of morphine in Sprague-Dawley rats

The teratogenic and postnatal developmental effects of morphine exposure during pregnancy were studied in Sprague-Dawley rats in three separate experiments using chronically implanted osmotic minipumps in order to avoid respiratory depression. In the first experiment, the teratogenic effects of three different morphine dosages were studied: a low dose (10 mg/kg/day), an intermediate dose (35 mg/kg/day), and a high dose (70 mg/kg/day). On day 5 of gestation, osmotic minipumps that deliver their contents at a constant rate for 15 days were implanted subcutaneously on the back of the rats. On day 20 of gestation, cesarean sections were performed, reproductive indices were determined, and fetuses were examined externally and then preserved for subsequent visceral and skeletal examinations. The pregnancy rate was significantly reduced at the intermediate and high doses to 57% and 6%, respectively (control, 83%). No teratogenic effects were observed at any dosage, but growth retardation was present in the intermediate-dose group. In the second experiment, postnatal survival of the offspring of dams treated with either normal saline, morphine (35 mg/kg/day), or the synthetic opioid, fentanyl (500 micrograms/kg/day) were studied. Offspring of morphine-treated dams had a significantly higher mortality rate, which peaked at 56% within 2 days. No effect was seen after fentanyl treatment. In the third experiment, pups of morphine-treated dams were cross-fostered by saline-treated dams; the postnatal mortality in offspring of morphine-treated dams remained high (62%). Our results indicate that doses of morphine up to 35 mg/kg/day delivered by osmotic minipumps are not teratogenic in rats but cause other adverse fetal effects that result in increased postnatal mortality.     

应用单细胞凝胶电泳研究甲醛的发育毒性(简报)

甲醛(HCHO)属于高挥发性极易溶于水的小分子醛类化合物,是人们日常生活中经常接触的一种空气污染物。甲醛可以引起各种相关疾病,2004年已被世界卫生组织提升为AI类化合物——人类致