Reproductive and neurobehavioural effects in three-generation toxicity study of piperonyl butoxide administered to mice

Piperonyl butoxide (PB) was administered continuously to mice from 5 weeks of age in the F₀ generation to weaning of the F₂ generation. PB was administered in the diet at levels of 0 (control), 0.1, 0.2, 0.4 and 0.8%. Selected reproductive, developmental and behavioural parameters were measured. Litter size and litter weight were reduced in higher-dosed groups, and the body weight of the pups in the lactation period was reduced in dosed pups in each generation. The survival index at postnatal day 21 of the group receiving 0.8% PB was reduced in each generation. The developmental and behavioural parameters in the lactation period were little different from those of the controls, apart from olfactory orientation in the F₁ generation. However, in the F₂ generation mice, surface righting, cliff avoidance and olfactory orientation were adversely affected in treatment groups. The results suggest that PB had adverse effects on reproductive, developmental and behavioural parameters of mice, with increasing effects in subsequent generations of offspring.     

Reproductive and neurobehavioural effects of phloxine administered to mice

The colour additive phloxine was given in the diet to provide dietary levels of 0 (control), 0.1, 0.3 and 0.9%, from 5 wk of age of the F₀ generation to 8 wk of age of the F₁ generation in mice, and selected reproductive and neurobehavioural parameters were measured. There was little effect of phloxine on either litter size or weight, or sex ratio, whereas the body weight of the pups in the lactation period was significantly increased in all treatment groups. Among the neurobehavioural parameters measured, surface righting at postnatal day 4 of male pups was significantly reduced in all treatment groups. Some parameters of the motor activity of pups at 3 wk of age differed from those of the controls; in particular, the average speed of movement male pups was significantly reduced in all treatment groups. The dose levels of phloxine in this study produced a few adverse effects in reproductive and neurobehavioural parameters in mice.     

Effects of piperonyl butoxide on F1 generation mice.

Piperonyl butoxide (PB), used in Japan as a pesticide synergist and food additive, was administered to mice from 5 weeks of age in the F0 generation to 9 weeks of age in the F1 generation, in the diet at levels of 0 (control), 0.15, 0.30 and 0.60%, and some reproductive, developmental and behavioral parameters were measured. Some parameters of open field activity were reduced in the treatment groups; in particular, ambulation and rearing were significantly reduced in F0 generation male mice and in 3-week-old F1 generation male mice. The weight of the pups was significantly reduced and litter weight tended to be reduced in the treatment groups. Body weight of dosed pups was reduced in the lactation period. Of the developmental parameters, olfactory orientation was significantly reduced as compared to controls. The dose levels of PB in this study, therefore, had an effect on some reproductive, developmental and behavioral parameters in mice.     

Reproductive and neurobehavioural toxicity study of bis(2-ethylhexyl) phthalate (DEHP) administered to mice in the diet.

Bis(2-ethylhexyl) phthalate (DEHP) was given in the diet to provide levels of 0 (control), 0.01, 0.03, and 0.09% from 5 weeks of age of the F0 generation to 9 weeks of age of the F1 generation in mice, and selected reproductive and neurobehavioural parameters were measured. There were no adverse effects of DEHP on either litter size, litter weight or sex ratio at birth. The average body weight of male offspring was significantly decreased in the low-dose group at birth. In behavioural developmental parameters, surface righting at PND 4 was significantly delayed in the low- and middle-dose group in female offspring, and those effects were slightly dose related (P < 0.05). Surface righting at PND 7 was significantly depressed in the high-dose group of male offspring, and those effects were significantly dose related (P < 0.001). That of female offspring was significantly depressed in the low-dose group. The dose level of DEHP in the present study produced few adverse effects in reproductive and neurobehavioural parameters in mice.     

Reproductive and neurobehavioural effects of bis(2-ethylhexyl) phthalate (DEHP) in a cross-mating toxicity study of mice.

Bis(2-ethylhexyl) phthalate (DEHP) was given in the diet to provide levels of 0% (C) or 0.03% (T) from 5 weeks of age of the F0 generation to 9 weeks of age of the F1 generation in mice. At 9 weeks of age, each female was paired with one male from the same or another treatment groups (cross-mating: C/C, T/C, C/T, T/T), for a period of 5 days. The selected reproductive and neurobehavioural parameters were measured. There were no adverse effects of DEHP on either litter size, litter weight and sex ratio at birth. The average body weight of female offspring was significantly affected in group IV (T/T) at PND 14. In behavioural developmental parameters, swimming direction at PND 4 was significantly accelerated in group III (C/T) in female offspring. In movement activity of exploratory behaviour at 3 weeks of age, number of movement of male offspring was significantly affected in group IV (T/T). The dose level of DEHP in the present cross-mating study produced few adverse effects in reproductive and neurobehavioural parameters in mice.     

Multigenerational exposure to phytosterols in the mouse

Due to beneficial health effects phytosterols (PS) are increasingly added to functional foods. The aim of the present study was to investigate the chronic effects of a dietary PS mixture (5 mg/kg/day), containing mainly β-sitosterol, on the reproduction of the mouse. General reproductive parameters, postnatal development, growth and survival of pups, weight of sex organs, the concentrations of plasma sex steroids and testicular testosterone were monitored across five generations (F₀–F₄). PS exposure increased the plasma levels of testosterone and decreased the relative uterine weights in the pups of F₂ and F₄ generations. Furthermore, PS exposure increased the concentrations of plasma estradiol in the female pups of F₃ generation. PS supplement also increased the testicular levels of testosterone in the male pups of F₂ generation. In spite of these transitory changes, PS exposure caused no permanent deleterious effects on the reproduction of the mouse.     

Caffeine-mediated effects on reproductive health over two generations in rats

The present study was designed to investigate the mechanism(s) underlying previously observed birth weight differences found in the first litter of the second (F₂) generation bred from caffeine-exposed F₁ females. The effect of exposure to caffeine in utero on subsequent sexual receptivity, fertility, gestation length, parturition, nesting activity, maternal behaviour, and reproductive senescence in the F₁ mothers, and the viability of the F₂ offspring was investigated. This information was collected by breeding control or caffeine exposed females for 8 consecutive litters. It was demonstrated that exposure to caffeine did not affect the sexual receptivity, fertility, gestation length, or maternal behaviour of the F₁ females, but parturition was prolonged and the viability of the F₂ generation was seriously jeopardised. Many F₂ pups were born significantly larger than their control counterparts and a significant proportion of litters (after the first two litters) were wholly stillborn. It was concluded that a changed genetic program, mediated via the F₂ fetus, delayed the normal progression of parturition. This, in turn, compromised the F₁ mothers and caused increased mortality of their offspring. The severity of the outcome was dose dependent.     

Reproductive and neurobehavioural toxicity study of tartrazine administered to mice in the diet.

Tartrazine was given in the diet to provide levels of 0% (control), 0.05%, 0.15%, and 0.45% (approximately 83, 259, 773 mg/kg/day, respectively) from five weeks of age of the F0 generation to nine weeks of age of the F1 generation in mice, and selected reproductive and neurobehavioural parameters were measured. In movement activity of exploratory behaviour in the F0 generation, number of vertical activity was significantly increased in the middle-dose group in males. There were no adverse effects of tartrazine on either litter size, litter weight and sex ratio at birth. The average body weight of male offspring was significantly increased in the high-dose group and that of female offspring was significantly increased in the middle-dose group at birth. In behavioural developmental parameters, surface righting at PND 4 was significantly accelerated in the high-dose group in male offspring, and those effects were significantly dose-related in a trend test (P<0.01). Cliff avoidance at PND 7 was significantly accelerated in the middle-dose group in male offspring. Negative geotaxis at PND 4 was significantly delayed in the high-dose group in female offspring. Other variables measured showed no significant adverse effects in either sex in the lactation period. In movement activity of exploratory behaviour in the F1 generation, number of movement showed a significant tendency to be affected in the treatment groups in male offspring in a trend test (P<0.05). The dose level of tartrazine in the present study produced a few adverse effects in neurobehavioural parameters during the lactation period in mice. Nevertheless, the high-dose level were in excess of the ADI of tartrazine (0-7.5 mg/kgbw), and the actual dietary intake of tartrazine is presumed to be much lower. It would therefore appear that the levels of actual dietary intake of tartrazine is unlikely to produce any adverse effects in humans.     

Reproductive and neurobehavioural toxicity study of erythrosine administered to mice in the diet.

Erythrosine was given in the diet to provide levels of 0 (control), 0.005, 0.015 and 0.045% from 5 weeks of age of the F(0) generation to 9 weeks of age of the F(1) generation in mice, and selected reproductive and neurobehavioural parameters were measured. There were no adverse effects of erythrosine on either litter size, litter weight or sex ratio at birth. The average body weight of the offspring was significantly increased in the middle-dose group in both sexes during the lactation period. In behavioural developmental parameters, any variables showed no significant adverse effects in either sex in the lactation period. In movement activity of exploratory behaviour, several parameters were significantly changed in the high-dose group, and those effects were dose related in adult females in the F(0) and F(1) generations and in male offspring in the F(1) generation. The dose level of erythrosine in the present study produced few adverse effects in reproductive and neurobehavioural parameters in mice.     

Toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin in the developing male Wistar(Han) rat. I: No decrease in epididymal sperm count after a single acute dose.

It has been reported that fetal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) causes defects in the male reproductive system of the rat. We set out to replicate and extend these effects using a robust experimental design. Groups of 75 (control vehicle) or 55 (50, 200, or 1000 ng of TCDD/kg bodyweight) female Wistar(Han) rats were exposed to TCDD on gestational day (GD)15, then allowed to litter. The high-dose group dams showed no sustained weight loss compared to control, but four animals had total litter loss. Pups in the high-dose group showed reduced body weight up till day 21, and pups in the medium dose group showed reduced body weight in the first week postpartum. Balano-preputial separation was significantly delayed in the high-dose group male offspring. There were no significant effects of treatment when the offspring were subjected to a functional observational battery or mated with females to assess reproductive capability. Twenty-five males per group were killed on postnatal day (PND) 70, and approximately 60 animals per group (approximately 30 for the high-dose group) on PND120 to assess seminology and other end points. At PND120, the two highest dose groups showed a statistically significant elevation of sperm counts, compared to control; however, this effect was small (approximately 30%), within the normal range of sperm counts for this strain of rat, was not reflected in testicular spermatid counts nor PND70 data, and is therefore postulated to have no biological significance. Although there was an increase in the proportion of abnormal sperm at PND70, seminology parameters were otherwise unremarkable. Testis weights in the high-dose group were slightly decreased at PND70 and 120, and at PND120, brain weights were decreased in the high-dose group, liver to body weight ratios were increased for all three dose groups, with an increase in inflammatory cell foci in the epididymis in the high-dose group. These data show that TCDD is a potent developmental toxin after exposure of the developing fetus but that acute developmental exposure to TCDD on GD15 caused no decrease in sperm counts.     

Evaluation of the reproductive and developmental toxicity of aluminium ammonium sulfate in a two-generation study in rats

Aluminium ammonium sulfate (AAS) was tested for reproductive/developmental toxicity in a two-generation study. Male and female rats were continuously given AAS in drinking water at 0, 50, 500 or 5000 ppm. Water consumption was decreased in all AAS-treated groups, and the body weight of parental animals transiently decreased in the 5000 ppm group. In either generation, no compound-related changes were found in estrous cyclicity, sperm parameters, copulation, fertility and gestation index, number of implantations and live birth pups, sex ratios of pups or viability during the preweaning period. Male and female F1 pups in the 5000 ppm group showed a lower body weight on postnatal day 21, while there were no differences in the birth weight of F1 and F2 pups between the control and AAS-treated groups. Preweaning body weight gain in F2 males and females indicated a similar decreasing tendency at 5000 ppm. In F1 and F2 weanlings, the weight of the liver, spleen and thymus decreased at 5000 ppm, but no histopathological changes were found in these organs. In F1 females in the 5000 ppm group, vaginal opening was delayed slightly. There were no compound-related changes in male preputial separation or in other developmental landmarks. In behavioral tests conducted for F1 animals at 4-6 weeks of age, no compound-related changes were found in spontaneous locomotor activity and performance in a water-filled multiple T-maze. In conclusion, the NOAEL of AAS for two-generation reproductive/developmental toxicity was considered to be 500 ppm in rats. Considering the aluminium content in the basal diet, the total ingested dose of aluminium from drinking water and food in this 500 ppm group was calculated to be 5.35 mg Al/kg bw/day.     

Multigeneration reproduction study of policosanol in rats

The hypocholesterolaemic drug policosanol was administered to Sprague-Dawley rats of both sexes throughout three successive generations at concentrations of 0, 5, 50 and 500 mg/kg bw/day by gavage. for each generation two litters were reared until they were at least 3 weeks old. No clinical signs which could be related to the administration of the test substance were observed in the F₀, F_1b and F_2b parents. There were no differences among groups in the number of animals that conceived, the number of pups born live or dead, the rate of male to female pups, the number of pups that survived until weaning and the pups' body weights through the lactancy. The following test showed no treatment-related effects on F3b offspring: righting on a surface, air righting, corneal, pirmal and pain reflexes, auditory startle and visual placing. The results of the present study did not demonstrate any deleterious effects on the fertility, reproductive performance or development of rats administered policosanol at levels of up to 500 mg/kg bw/day over three successive generations.     

The effects of perinatal/juvenile heptachlor exposure on adult immune and reproductive system function in rats.

This study was performed to determine if developmental exposure of rats to heptachlor (H) during the last half of gestation through puberty adversely affects adult functioning of the immune and reproductive systems. Time-bred pregnant female Sprague-Dawley rats were dosed by gavage with H (0, 30, 300, or 3000 microg/kg/day) from gestation day (GD) 12 to postnatal day (PND) 7, followed by direct dosing of the pups with H through PND 42. Separate groups of rats were evaluated with a battery of immune function tests, while other groups of rats were evaluated for reproductive development and function. Additional groups of rats were euthanized at the end of the dosing period for histological analyses of major organ systems. Some dams and PND 7 pups were euthanized; milk, plasma, fat and/or tissues were assayed for H and heptachlor epoxide B (HEB), a major metabolite of H. The amount of H and HEB found in milk, blood, fat, and tissues was proportional to the dose of H administered. There were no effects on the number or survival of pups born to H-exposed dams nor to pups exposed postnatally. There were no effects on the number of treated dams delivering litters or on litter size, nor were there any effects on any of the reproductive end points examined in the F(0) or F(1) rats. There were no effects of H exposure on lymphoid organ weights, splenic natural killer (NK) cell activity, and splenic lymphoproliferative (LP) responses to mitogens and allogeneic cells in a mixed lymphocyte response (MLR) assay at 8 weeks of age. H exposure did not alter delayed or contact hypersensitivity at 10 or 17 weeks of age, respectively. However, the primary IgM antibody response to sheep red blood cells (SRBCs) was suppressed in a dose-dependent manner in males, but not females, at 8 weeks of age. The percentage of B lymphocytes (OX12(+)OX19(-)) in spleen was also reduced in the high-dose males. The anti-SRBC IgM response was reduced only in males exposed to 30 microg H/kg/day in a separate group of rats 21 weeks of age. In these same rats, at 26 weeks of age, the secondary IgG antibody response to SRBCs was suppressed in all of the H-exposed males, but not females. These data indicate that perinatal exposure of male rats to H results in suppression of the primary IgM and secondary IgG anti-SRBC responses. Suppression of these antibody responses persisted for up to 20 weeks after the last exposure to H, at a total exposure of approximately 1500 microg H/kg/rat.     

Fertility and developmental neurotoxicity effects of inhaled hydrogen sulfide in Sprague-Dawley rats

In this study, we examined whether perinatal exposure by inhalation to hydrogen sulfide (H2S) had an adverse impact on pregnancy outcomes, offspring prenatal and postnatal development, or offspring behavior. Virgin male and female Sprague-Dawley rats (12 rats/sex/concentration) were exposed (0, 10, 30, or 80 ppm H2S; 6 h/day, 7 days/week) for 2 weeks prior to breeding. Exposures continued during a 2-week mating period (evidence of copulation = gestation day 0 = GD 0) and then from GD 0 through GD 19. Exposure of dams and their pups (eight rats/litter after culling) resumed between postnatal day (PND) 5 and 18. Adult male rats were exposed for 70 consecutive days. Offspring were evaluated using motor activity (PND 13, 17, 21, and 60+/-2), passive avoidance (PND 22+/-1 and 62+/-3), functional observation battery (PND 60+/-2), acoustic startle response (PND 21 and 62+/-3), and neuropathology (PND 23+/-2 and 61+/-2). There were no deaths and no adverse physical signs observed in F0 male or female rats during the study. A statistically significant decrease in feed consumption was observed in F0 male rats from the 80-ppm H2S exposure group during the first week of exposure. There were no statistically significant effects on the reproductive performance of the F0 rats as assessed by the number of females with live pups, litter size, average length of gestation, and the average number of implants per pregnant female. Exposure to H2S did not affect pup growth, development, or performance on any of the behavioral tests. The results of our study suggest that H2S is neither a reproductive toxicant nor a behavioral developmental neurotoxicant in the rat at occupationally relevant exposure concentrations (< or =10 ppm).     

Reproductive and neurobehavioural toxicity study of Ponceau 4R administered to mice in the diet.

Ponceau 4R was given to mice in the diet at levels of 0 (control), 0.12%, 0.24%, and 0.48% from 5 weeks of age of the F(0) generation to 9 weeks of age of the F(1) generation, and selected reproductive and neurobehavioural parameters were measured. There was no adverse effect of Ponceau 4R on litter size, litter weight or sex ratio at birth. The average body weight of male and female offspring was increased significantly in the high-dose group at postnatal days (PNDs) 0, 4 and 21. In behavioural developmental parameters, surface righting at PND 4 was affected significantly in the high-dose group in male offspring. Other variables measured showed no consistently significant adverse effect on either sex in the lactation period. In multiple water T-maze performance in the F(1) generation, the time taken was significantly longer than the control in the middle-dose and high-dose groups in males, and those effects were significantly dose-related (P<0.01). The dose level of Ponceau 4R in the present study produced no adverse effect on reproduction, and a few adverse effects on neurobehavioural parameters in mice. The non-observed adverse effect level (NOAEL) was presumed to be 0.12% in the diet (approximately 205mg/kg per day) for maze learning by males in the F(1) generation. Nevertheless, the middle-dose and high-dose levels were in excess of the acceptable daily intake (ADI) of Ponceau 4R (0-4.0mg/kg body weight), and the actual dietary intake of Ponceau 4R in humans is presumed to be much lower. It would appear, therefore, that the level of dietary intake of Ponceau 4R is unlikely to produce any adverse reproductive or neurobehavioural effect in humans.     

Acute toxicity of textile dye wastewaters (untreated and treated) of Sanganer on male reproductive systems of albino rats and mice

This study reports on the toxic effects of 15-days oral administration of untreated (Influent) and treated (Effluent) textile dye wastewaters on male reproductive systems of adult Swiss albino rats (age: 85–90 days) and mice (40–50 days). Textile dye wastewaters decreased body weight (7–25%) and reproductive organ weight (testis, epididymis, prostate gland and seminal vesicle, 2–48%). Similar trends were noted for total protein (14–70%), cholesterol (14–91%) and total lipid (10–30%) content of reproductive organs and spermatozoa, and for fructose levels in seminal vesicle (18–44%). Acid phosphatase activity in prostate however, was increased (11–44%) in the wastewater-exposed animals. Histopathological studies of treated animals revealed altered spermatogenesis, with higher sperm abnormalities, reduction in sperm counts (10–59%), and altered motility (14–56%). The magnitude of these abnormalities was stronger in rats versus mice, while among treatments, it was stronger in the Influent animals. Adverse effects improved when treated rats were allowed to recover 45 days in the control condition. Only recovered Effluent rats were capable of fertilizing normal females indicating that treated wastewater was less toxic; however, in comparison to control rats, litter size and body weight gains of F₁ and F₂ generations were adversely affected. Thus, the present study has established toxicity of both untreated and treated textile dye wastewater on reproductive biology of male Albino mice and rats.     

Three-generation reproductive toxicity study of dietary bisphenol A in CD Sprague-Dawley rats.

Bisphenol A (BPA) was evaluated at concentrations of 0, 0.015, 0.3, 4.5, 75, 750, and 7500 ppm ( approximately 0.001, 0.02, 0.3, 5, 50, and 500 mg/kg/day of BPA) administered in the diet ad libitum to 30 CD((R)) Sprague-Dawley rats/sex/dose for 3 offspring generations, 1 litter/generation, through F3 adults. Adult systemic toxicity at 750 and 7500 ppm in all generations included: reduced body weights and body weight gains, reduced absolute and increased relative weanling and adult organ weights (liver, kidneys, adrenals, spleen, pituitary, and brain), and female slight/mild renal and hepatic pathology at 7500 ppm. Reproductive organ histopathology and function were unaffected. Ovarian weights as well as total pups and live pups/litter on postnatal day (PND) 0 were decreased at 7500 ppm, which exceeded the adult maximum tolerated dose (MTD). Mating, fertility, gestational indices; ovarian primordial follicle counts; estrous cyclicity; precoital interval; gestational length; offspring sex ratios; postnatal survival; nipple/areolae retention in preweanling males; epididymal sperm number, motility, morphology; daily sperm production (DSP), and efficiency of DSP were all unaffected. At 7500 ppm, vaginal patency (VP) and preputial separation (PPS) were delayed in F1, F2, and F3 offspring, associated with reduced body weights. Anogenital distance (AGD) on PND 0 was unaffected for F2 and F3 males and F3 females (F2 female AGD was increased at some doses, not at 7500 ppm, and was considered not biologically or toxicologically relevant). Adult systemic no observed adverse effect level (NOAEL) = 75 ppm (5 mg/kg/day); reproductive and postnatal NOAELs = 750 ppm (50 mg/kg/day). There were no treatment-related effects in the low-dose region (0.001-5 mg/kg/day) on any parameters and no evidence of nonmonotonic dose-response curves across generations for either sex. BPA should not be considered a selective reproductive toxicant, based on the results of this study.     

Evaluation of the Reproductive and Developmental Toxicity of a Fluoroalkylethanol Mixture

The objective of these studies was to evaluate the reproductive and developmental toxicity of a commercial fluoroalkylethanol mixture, which is an intermediate in the production of fluorotelomers. The test substance was administered daily by gavage to Sprague–Dawley rats as a suspension in 0.5% aqueous methylcellulose. In a one-generation reproductive toxicity study, rats (20 per sex per group) were given dosages of 0, 25, 100, or 250 mg kg^{? 1} day^{? 1} for a period of 74 days prior to cohabitation, and during mating, gestation, and lactation. Body weights, feed consumption, clinical signs, gross pathology, sperm parameters, estrous cyclicity, and reproductive performance were evaluated for the P₁ generation. The F₁ offspring were evaluated during the lactation period for growth and survival and given a gross pathology examination at weaning. A subset of the offspring were retained; body weights, feed consumption, clinical signs, and age at onset of vaginal opening and preputial separation were evaluated, and gross pathology was performed on postnatal day 60. In the developmental toxicity study, groups of time-mated Sprague–Dawley female rats were given the test substance as a suspension in 0.5% aqueous methylcellulose at daily dosages of 0, 50, 200, or 500 mg kg^{? 1} day^{? 1} by gavage on gestation days 6–20. During the in-life portion of the study, growth parameters and clinical observations were made. On gestation day 21, dams were euthanized, and the thoracic and abdominal viscera were examined. The uterine contents were removed and examined, and fetuses were evaluated for any alterations. In the reproduction study, litter size at birth, number of live pups per litter on day 0 and 4 of lactation, and pup weights during lactation were reduced in groups administered ≥ 100 mg kg^{? 1} day^{? 1}. No other reproductive parameters were affected. There were no adverse reproductive effects observed at 25 mg kg^{? 1} day^{? 1}. In the developmental toxicity study, reduced maternal body weight parameters, increased perineal fur staining, and increased fetal skeletal alterations were observed at 500 mg kg^{? 1} day^{? 1}. There was no maternal or developmental toxicity at 50 or 200 mg kg^{? 1} day^{? 1}. Under the conditions of the studies, the no-observed adverse effect levels for this mixture were 25 mg kg^{? 1} day^{? 1} for subchronic toxicity and reproductive parameters and 200 mg kg^{? 1} day^{? 1} for developmental toxicity end points. No functional reproductive or developmental effects were observed at dose levels that did not adversely affect adult animals.     

Effects of tartrazine on exploratory behavior in a three-generation toxicity study in mice

Tartrazine was given to mice in the diet at levels of 0 (control), 0.05%, 0.15%, and 0.45% from 5 weeks of age of the F(0) generation to 9 weeks of age of the F(2) generation, and selected reproductive and neurobehavioral parameters were measured. In the F(1) generation, the development of swimming direction at postnatal day (PND) 7 was accelerated significantly in male offspring in a dose-related manner. Surface righting at PND 7 was affected significantly in female offspring in dose-related manner. Several variables in exploratory behavior showed significant tendencies to be affected in the treatment groups in male offspring at 3 weeks of age. In the F(2) generation, the development of swimming direction at PND 7 was accelerated significantly in the high-dosed group in male offspring. Time taken of olfactory orientation at PND 14 was accelerated significantly in male offspring in a dose-related manner. Several variables in exploratory behavior showed significant tendencies to be affected in the treatment groups in male offspring at 3 weeks of age, and in males at 8 weeks of age. The dose levels of tartrazine in the present study produced a few adverse effects on neurobehavioral parameters throughout generations in mice.     

Protective effects of vitamin E against reproductive toxicity induced by di(2-ethylhexyl) phthalate via PPAR-dependent mechanisms

Objective: To investigate the protective/ameliorative effects of vitamin E on di-2-(ethylhexyl) phthalate (DEHP)-induced reproductive toxicity, particularly in testicular toxicity in male rats, emphasizing peroxisome proliferator-activated receptor (PPAR)-dependent mechanism.

Methods: Sprague-Dawley females were exposed by oral route to DEHP alone or associated with vitamin E from gestation day (GD) 12.5 to postnatal day (PND) 3 according to the following treatment regimens: vehicle control (corn oil), vitamin E (200?mg/kg)+corn oil, DEHP (500?mg/kg)+corn oil, and DEHP (500?mg/kg)+vitamin E (200?mg/kg)+corn oil. Variables including litter size, sex ratio, pup weight, post-implantation losses, and the number of viable pups were also assessed. Three male pups per litter were randomly selected and necropsied to measure paired testes weight, apoptosis, and gene expression on PND 3. To evaluate the long-term protective effects of vitamin E, three randomly selected males were necropsied to measure testis histology on PND 70.

Results: Supplementation of vitamin E (200?mg/kg) reduced malformations, increased testes weight and prevented the maternal bodyweight loss induced by DEHP. Litter size, sex ratio, and number of viable pups were unaffected, but vitamin E co-administration declined testicular cell apoptosis, decreased the PPARs expression, and protected testis histology.

Conclusions: Vitamin E cotreatment showed protective effects against DEHP-induced testicular toxicity, including reproductive malformations, testicular weight, apoptosis and histology, and the mechanisms maybe associated with PPARs.