Two-generation reproduction toxicity studies of di-(C(7)-C(9) alkyl) phthalate and di-(C(9)-C(11) alkyl) phthalate in the rat

Di-(C(7)-C(9) alkyl) phthalate (D79P) and di-(C(9)-C(11) alkyl) phthalate (D911P), based on high-normality linear oxo-alcohols, have been assessed for their impact upon reproductive performance in Sprague-Dawley rats. Rats were continuously exposed to either D79P or D911P at dietary levels of 0%, 0.1%, 0.5%, or 1.0% over two generations. Selected F(0) offspring (F(1) generation) were exposed to the same dietary concentration of D79P or D911P as the respective F(0) animals, and were mated to produce F(1) offspring. Both D79P and D911P markedly reduced body weight gain in F(0) and F(1) adult males at the highest dose, but females were affected to a lesser extent. There was no impairment of fertility, fecundity, or development in either generation, but body weights of offspring in the 1.0% D79P and 1.0% D911P groups were slightly and transiently reduced over the weaning period. Although decreases in the weight of several organs were accounted for by depressed body weight, ovary weights were reduced in both generations exposed to 1.0% D79P, and epididymidal weights were slightly reduced in adults of both generations exposed to 1.0% D911P. However, ovarian function-assessed by the oestrus cycle and mating behaviour-and epididymidal sperm concentration, motility, and morphology were unaffected by either substance. Treatment resulted in liver changes, particularly in males, characterised by increased liver weight in young animals, histopathologic changes and reduced organ weight in mature animals, and an increase in palmitoyl CoA oxidase activity. In conclusion, neither D79P nor D911P impaired reproductive function in rats when administered in the diet at levels that induce systemic toxicity, and the NOAEL for effects on reproduction in the rat is 0.5% for both D79P and D911P.     

Dose-related effect by maternal exposure to di-(2-ethylhexyl) phthalate plasticizer on inducing hypospadiac male rats

The aim of this study was to evaluate dose-related effects on external genitalia of adult male offspring rats by maternal exposure to di-(2-ethylhexyl) phthalate (DEHP) plasticizer. Timed-pregnant rats were given DEHP by gastric intubation at doses of 0, 500, 750 or 1000 mg/kg body weight/day from gestation day 12–19 to establish a hypospadiac rat model. The hypospadias was observed and the incidence in three DEHP dosage levels was 10.7%, 30.6% and 37.0%, respectively. With exposed dose increased, mild, moderate and severe hypospadiac rats were distinguished and an increased incidence of severe hypospadias was observed. The other reproductive lesions like reduced penile length and anogenital distance/body weight were observed. The results indicated the dose-related external genitalia teratogenic toxicity, and graded hypospadias on male offspring was resulted from high dosage DEHP maternal exposure.     

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.     

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.     

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.     

Urinary and amniotic fluid levels of phthalate monoesters in rats after the oral administration of di(2-ethylhexyl) phthalate and di-n-butyl phthalate

Two studies were designed to examine amniotic fluid and maternal urine concentrations of the di(2-ethylhexyl) phthalate (DEHP) metabolite mono(2-ethylhexyl) phthalate (MEHP) and the di-n-butyl phthalate (DBP) metabolite monobutyl phthalate (MBP) after administration of DEHP and DBP during pregnancy. In the first study, pregnant Sprague-Dawley rats were administered 0, 11, 33, 100, or 300 mg DEHP/kg/day by oral gavage starting on gestational day (GD) 7. In the second study, DBP was administered by oral gavage to pregnant Sprague-Dawley rats at doses of 0, 100, or 250 mg/kg/day starting on GD 13. Maternal urine and amniotic fluid were collected and analyzed to determine the free and glucuronidated levels of MEHP and MBP. In urine, MEHP and MBP were mostly glucuronidated. By contrast, free MEHP and free MBP predominated in amniotic fluid. Statistically significant correlations were found between maternal DEHP dose and total maternal urinary MEHP (p=0.0117), and between maternal DEHP dose and total amniotic fluid MEHP levels (p=0.0021). Total maternal urinary MEHP and total amniotic fluid MEHP levels were correlated (Pearson correlation coefficient=0.968). Statistically significant differences were found in amniotic MBP levels between animals within the same DBP dose treatment group (p<0.0001) and between animals in different dose treatment groups (p<0.0001). Amniotic fluid MBP levels increased with increasing DBP doses, and high variability in maternal urinary levels of MBP between rats was observed. Although no firm conclusions could be drawn from the urinary MBP data, the MEHP results suggest that maternal urinary MEHP levels may be useful surrogate markers for fetal exposure to DEHP.     

Developmental toxicity of butyl benzyl phthalate in the rat using a multiple dose study design

The developmental toxicity of butyl benzyl phthalate (BBP) was investigated in the rat using ten dose groups between 270 and 2100 mg/kg/day. Exposure was by daily gavage from gestation day 5 through 16 or gestation day 5 through 20. Dose-response data were analyzed using the benchmark approach by fitting dose-response models to the various endpoints. BBP induced increased liver and kidney weights in dams, accompanied by liver enzyme increases in maternal serum. Extramedullary hematopoiesis, which was already substantial in control pregnant animals, was increased after BBP treatment. Fetotoxicity included increased resorptions, reduced fetal weights, increased incidence of skeletal anomalies, and reduced fetal testis weights in the presence of an increased incidence of retarded testicular descent. As embryotoxicity was found at lower dosages compared to observed maternal toxicity, BBP appeared to be a specifically embryotoxic compound. The extended exposure protocol (gestation day 5 through 20) appeared more sensitive for measuring fetotoxic effects. We recommend the use of more doses in toxicity tests, together with the benchmark approach as an appropriate and more accurate method for analyzing dose-response data compared to the NOAEL approach.     

Developmental Toxicity Evaluation of Ethylene Glycol by Gavage in New Zealand White Rabbits

Artificially inseminated New Zealand white (NZW) rabbits wereadministered ethylene glycol (EG) by gavage on Gestational Days(GD) 6 through 19 at doses of 0, 100, 500, 1000, or 2000 mg/kg/day,with 23–24 inseminated animals per group. Clinical signswere recorded and water consumption was measured daily; doeswere weighed on GD 0, 6–19, 25, and 30. At necropsy (GD30), maternal liver, kidney, and gravid uterine weights wererecorded. Histopathologic examination was performed on kidneysfrom 10 does/dose and for all unscheduled deaths. Ovarian corporalutea were counted and uterine implantation sites (total sites,resorptions, dead and live fetuses) were recorded. All livefetuses were weighed, sexed, and examined for external, visceral,and skeletal malformations and variations. EG resulted in profoundmaternal toxicity at 2000 mg/kg/day (42% mortality; three earlydeliveries and one spontaneous abortion) associated with renalpathology and unaccompanied by any other indicators of maternaltoxicity. Renal lesions at 2000 mg/kg/day involved the corticalrenal tubules and included intraluminal oxalate crystals, epithelialnecrosis, and tubular dilatation and degeneration. No dose-relatedmaternal toxicity occurred at 100–1000 mg/kg/day. Therewas no indication of developmental toxicity at any dose tested,including no effects on pre- or postimplantation loss, numberof fetuses, fetal body weight, or sex ratio (% male fetuses)per litter, and no evidence of teratogenicity. The "no observableadverse effect level" (NOAEL) for maternal toxicity was therefore1000 mg/kg/day and the NOAEL for developmental toxicity wasat least 2000 mg/kg/day in this study. The sensitivity of NZWrabbits relative to that of Sprague—Dawley rats and Swissmice for maternal and developmental toxicity from gavage administrationof EG during organogenesis can be determined for maternal toxicity:rabbits>mice>rats, and for developmental toxicity, mice>>rats >> rabbits.     

Teratogenicity of di-(2-ethylhexyl)phthalate in mice

Fetotoxicity of di-(2-ethylhexyl)phthalate (DEHP) was studied in a random strain (ddY-Slc♀ × CBA ♂) of mice. A single oral administration of DEHP 0.05 ml/kg on day 7 of gestation resulted in a decrease in body weight of live fetuses, but there were no dead, gross, or skeletal abnormal fetuses. At 0.1 ml/kg and above DEHP decreased fetal body weight and the fetuses were dead or deformed. The fetotoxicity was dose dependent and a straight line Y = 51.9 log X + 61.6 was obtained where Y = the rate of death(%) and X = the dose of DEHP administered (ml/kg). The LD₅₀ and the non-effective aximum dose which induced fetal death was 0.60 ml/kg and 0.065 ml/kg, respectively. The non-effective maximum doses which resulted in gross and skeletal abnormalities were 0.80 and 0.68 ml/kg, respectively.     

Developmental Toxicity of 1,2-Dichloropropane (PDC) in Rats and Rabbits Following Oral Gavage

1,2-Dichloropropane (PDC) was evaluated for its potential causeembryonal/fetal toxicity and teratogenicity in pregnant ratsand rabbits. PDC was administered via oral gavage at dose levelsof 0, 10, 30, or 125 mg/kg/day on Days 6 through 15 of gestation(rats) or 0, 15, 50, or 150 mg/kg/day on gestation Days 7 through19 (rabbits). Fetuses were examined on Gestation Day 20 (rats)or Day 28 (rabbits). Maternal toxicity was observed in bothrats and rabbits at the high dose levels. Rats given 125 mg/kg/dayof PDC showed clinical signs of toxicity and decreased bodyweight and body weight gain. Rabbits given 150 mg/kg/day PDCshowed changes in hematologic parameters and decreased bodyweight gain. Although maternal toxicity was apparent, no indicationteratogenicity was observed in rat or rabbit fetuses at anydose level. Significant increases in the incidence of delayedossification of skull bones, considered secondary to decreasedmaternal body weight gain, were observed in rats given 125 mg/kg/dayand rabbits given 150 mg/kg/day. No maternal or developmentaleffects were observed in rats given 10 or 30 mg/kg/day or inrabbits given 15 or 50 mg/kg/day of PDC. Based on the resultsof these studies the maternal and developmental NOELs in ratsand rabbits were 30 and 50 mg/kg/day, respectively.     

Investigations on the effects of alkyl polyglucosides on development and fertility.

Alkyl polyglucosides are non-ionic surfactants which are mainly used in laundry detergents, hard surface cleaners and personal care products. Two in vitro screening test systems were used to investigate the endocrine modulating potential of alkyl polyglucosides. No indications were observed for any estrogenic or anti-estrogenic effects in an MCF-7 E-Screen assay and a reporter gene assay using luciferase-transfected MCF-7 cells. Concentrations exceeding the effect concentration of estradiol by a factor of 1000 did not reveal any indication for an estrogenic activity. Furthermore, in a combination assay investigating the effects of estradiol in the presence of alkyl polyglucoside, no anti-estrogenic potential was observed. In an one-generation screening assay in rats no effects on the fertility were observed up to the highest dose of 1000 mg/kg bw/day alkyl glucoside. Potential embryo-/fetotoxicity and/or teratogenicity was investigated in a segment II study in rats. No effects were noted up to the limit dose of 1000 mg/kg bw/day. All parameters of the treatment groups were comparable with those of the control group. Skeletal and visceral investigations did not detect any treatment-related malformations. For the embryo/fetotoxicity, the teratogenicity and the maternal toxicity a NOAEL of 1000 mg/kg was deduced.     

Altered gene profiles in fetal rat testes after in utero exposure to di(n-butyl) phthalate.

Di(n-butyl) phthalate (DBP) has antiandrogenic-like effects on the developing reproductive tract in the male rat and produces regions of interstitial cell hyperplasia and gonocyte degeneration in the developing fetal testes at maternal doses of 100-500 mg/kg/day. Neither DBP nor its primary metabolites interact with the androgen receptor in vitro. The present study was performed to examine gene expression in the fetal rat testes following in utero DBP exposure. Pregnant Sprague-Dawley rats received corn oil, DBP (500 mg/kg/day), or flutamide (reference antiandrogen, 50 mg/kg/day) by gavage daily from gestation day (GD) 12 to 21. Dose levels were selected to maximize fetal response with minimal maternal toxicity. Testes were isolated on GD 16, 19, and 21. Global changes in gene expression were determined by microarray analysis. Selected genes were further examined by quantitative RT-PCR. DBP, but not flutamide, reduced expression of the steroidogenic enzymes cytochrome P450 side chain cleavage, cytochrome P450c17, and steroidogenic acute regulatory protein. Testicular testosterone and androstenedione were decreased on GD 19 and 21, while progesterone was increased on GD 19 in DBP-exposed testes. Testosterone-repressed prostate message-2 (TRPM-2) was upregulated, while c-kit (stem cell factor receptor) mRNA was downregulated following DBP exposure. TRPM-2 and bcl-2 protein staining was elevated in GD 21 DBP-exposed Leydig and Sertoli cells. Results of this study have led to the identification of several possible mechanisms by which DBP can induce its antiandrogenic effects on the developing male reproductive tract without direct interaction with the androgen receptor. Our results suggest that the antiandrogenic effects of DBP are due to decreased testosterone synthesis. In addition, enhanced expression of cell survival proteins such as TRPM-2 and bcl-2 may be involved in DBP-induced Leydig cell hyperplasia, whereas, downregulation of c-kit may play a role in gonocyte degeneration. Future studies will explore the link between these identified gene expression alterations and ultimate adverse responses.     

A dose response study following in utero and lactational exposure to di-(2-ethylhexyl) phthalate (DEHP): reproductive effects on adult male offspring rats

The reproductive effects of in utero and lactational exposure to di-(2-ethylhexyl) phthalate (DEHP) in adult male offspring rats were investigated. The selected endpoints included reproductive organ weights, testicular function, hormonal status, sexual behaviour and fertility. Two wide ranges of doses, low and high, were tested. Female Wistar rats were treated daily with DEHP and peanut oil (vehicle control) by gavage from gestation day 6 to lactation day 21. The low-doses were 0.015, 0.045, 0.135, 0.405 and 1.215 mg DEHP/kg body weight (bw)/day, and the high-doses were 5, 15, 45, 135 and 405 mg DEHP/kg bw/day. A reduction in daily sperm production of 19-25% in relation to control was observed in animals exposed to 15, 45, 135 and 405 mg/kg/day. Quantitation of specific cell types shows that the observed effects in daily sperm production are not related to changes in the number of Sertoli cells or their capability to support early stages spermatocytes. A low incidence of cryptorchidism was observed in DEHP exposed groups with a lowest observed adverse effect level of 5mg/kg/day. Serum testosterone concentration was similar to control at most doses but was significantly increased at 0.045, 0.405 and 405 mg DEHP/kg/day. In spite of this effect, the weight of seminal vesicle with coagulating glands was significantly reduced at 405 mg/kg/day. Testis, epididymis and prostate weights were similar among groups. Fertility and sexual behaviour were not affected by DEHP treatment at any dose. Overall, our results show that in utero and lactational DEHP exposure reduces daily sperm production and has the potential to induce reproductive tract abnormalities (of which cryptorchidism seems to be the most sensitive in our rat strain) in male offspring rats. The lowest observed adverse effect levels (LOAELs) for these effects were 15 and 5 mg/kg/day, respectively. Therefore, the no observed adverse effect level (NOAEL) for this study can be set at 1.215 mg/kg/day.     

Testicular toxicity induced by single dosing of di- and mono-(2-ethylhexyl) phthalate in the rat

The testicular toxicity of di-(2-ethylhexyl) phthalate (DEHP), a widely used plasticizer, and of its major metabolite, mono-(2-ethylhexyl) phthalate (MEHP), was assessed after a single dose in rats. Treatment with a single dose of 2.8 g/kg DEHP or 0.8 g/kg MEHP was sufficient to induce testicular atrophy as observed 7 days after dosing. Such a treatment had no effect on plasma FSH levels, and had varying effects on testicular zinc concentrations. After a single dose of 0.8 g/kg MEHP the testicular toxicity was age-dependent, in that only prepubertal rats were susceptible.     

Reproductive toxicity evaluation of dietary butyl benzyl phthalate (BBP) in rats

Butyl benzyl phthalate (BBP) was administered in the diet at 0, 750, 3750, and 11,250 ppm ad libitum to 30 rats per sex per dose for two offspring generations, one litter/breeding pair/generation, through weaning of F2 litters. Adult F0 systemic toxicity and adult F1 systemic and reproductive toxicity were present at 11,250 ppm (750 mg/kg per day). At 11,250 ppm, there were reduced F1 and F2 male anogenital distance (AGD) and body weights/litter during lactation, delayed acquisition of puberty in F1 males and females, retention of nipples and areolae in F1 and F2 males, and male reproductive system malformations. At 3750 ppm (250 mg/kg per day), only reduced F1 and F2 offspring male AGD was present. There were no effects on parents or offspring at 750 ppm (50 mg/kg per day). The F1 parental systemic and reproductive toxicity no observable adverse effect level (NOAEL) was 3750 ppm. The offspring toxicity NOAEL was 3750 ppm. The offspring toxicity no observable effect level (NOEL) was 750 ppm, based on the presence of reduced AGD in F1 and F2 males at birth at 3750 ppm, but no effects on reproductive development, structures, or functions.     

Effect of butyl benzyl phthalate on reproduction and zinc metabolism

Butyl benzyl phthalate (BBP) has been shown to be teratogenic. One mechanism contributing to the teratogenicity of several developmental toxicants, is chemical-induced changes in maternal zinc (Zn) metabolism which result in an increased synthesis of maternal liver metallothionein (Mt), and a subsequent reduction in Zn delivery to the conceptus. We investigated the effects of maternal BBP exposure on maternal-fetal Zn metabolism in Wistar rats. In study I, dams were gavaged with BBP (0,250,1000,1500 or 2000 mg/kg) on gestation days (GD) 11 through 13, and killed on GD 20. Maternal toxicity was evident in the three highest dose groups. Embryo/fetal death and small pup weights and lengths were noted in the 2000 mg BBP/kg group. Fetuses in the 1500 and 2000 mg/kg groups were characterized by poor skeletal ossification, and a high frequency of cleft palate. Rib anomalies were observed in the three highest dose groups. Maternal liver Mt concentrations were only slightly elevated in the 1500 and 2000 mg/kg groups. In study II, dams treated as above, were gavaged with 65Zn and killed 18 h later. While the 2000 mg/kg group had high percentages of 65Zn in some maternal tissues, sequestration of 65Zn in maternal liver was not evident. Thus, BBP is not a strong inducer of Mt, and the teratogenicity of BBP does not appear to be due to alterations in maternal and/or embryonic Zn metabolism.     

Effects of prenatal exposure to the environmental pollutant 2-bromopropane on embryo-fetal development in rats

2-Bromopropane (2-BP), a halogenated propane analogue, is a substitute for chlorofluorocarbones. The present study was carried out to investigate the potential adverse effects of 2-BP on pregnant dams and embryo-fetal development after maternal exposure on gestational days (GD) 6 through 19 in Sprague-Dawley rats. The test chemical was administered subcutaneously to pregnant rats at dose levels of 0, 250, 500, and 1000 mg/kg per day. All dams were subjected to caesarean section on GD 20 and their fetuses were examined for external, visceral and skeletal abnormalities. In the 1000 mg/kg group, maternal toxicity included an increase in the incidence of abnormal clinical signs, a suppression in the body weight and body weight gain, and a decrease in the food intake. Developmental toxicity included an increase in the fetal deaths, a decrease in the litter size, and a reduction in the fetal body weight. In addition, an increase in the incidence of fetal external, visceral, and skeletal abnormalities was seen. In the 500 mg/kg group, minimal developmental toxicity including decreased fetal body weight and increased fetal ossification delay was observed. There were no adverse effects on either pregnant dams or embryo-fetal development in the 250 mg/kg group. These findings suggest that a 14-day subcutaneous dose of 2-BP is embryotoxic and teratogenic at a maternally toxic dose (i.e., 1000 mg/kg per day) and is minimally embryotoxic at a nonmaternally toxic dose (i.e., 500 mg/kg per day) in Sprague-Dawley rats. In the present experimental conditions, the no-observed-adverse-effect level (NOAEL) of 2-BP is considered to be 500 mg/kg per day for dams and 250 mg/kg per day for embryo-fetal development.     

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.     

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.     

Study on developmental abnormalities in hypospadiac male rats induced by maternal exposure to di-n-butyl phthalate (DBP)

The objective of this study was to establish a hypospadiac rat model by maternal exposure to di-n-butyl phthalate (DBP) and to evaluate the developmental abnormalities of hypospadiac male rats. Timed-pregnant rats were given DBP by gastric intubation at doses of 0, 250, 500, 750 or 1000 mg/kg body weight (bw)/day from gestation day (GD) 14 to 18 to establish a hypospadiac rat model. The hypospadias was observed in the 500 and 750 mg/kg bw/day groups, the incidence of which was 6.8 and 41.3%, respectively. Transverse serial histological analysis of genitalia of hypospadiac male rats confirmed the malformation. With exposed dose increasing, the serum testosterone (T) levels of male rats inversely decreased, and in the same dosage group the serum T levels of hypospadiac rats were significantly lower than the levels of nonhypospadiac counterparts. The other reproductive lesions such as cryptorchidism and decreased ratio of anogenital distance/body weight (AGD/bw) were also observed. Autopsy analysis revealed the development of reproductive organs (prostate, testes, epididymis, pituitary gland) and nonreproductive organs (adrenal gland, liver, kidney, heart, spleen) of hypospadiac rats and nonhypospadiac counterparts. The results indicated that the reproductive system and developmental condition of hypospadiac male offspring were damaged severely by DBP.