Search

Prenatal exposure to phthalates is associated with reproductive and metabolic systems alterations. We investigated the effects of in utero and lactational exposure to Di-(2-ethyl-hexyl) phthalate (DEHP) and Di-n-butyl phthalate (DBP) on the reproductive system and glycemic homeostasis in male and female offspring of rats. Pregnant rats were exposed to equimolar doses (0.018, 0.18 and 1.8 mmol/kg/day) of DEHP or DBP corresponding to 7, 70, and 700 mg/kg/day for DEHP and 5, 50, and 500 mg/kg/day for DBP, respectively, by oral gavage from gestation day 13 to postnatal day 21, and using canola oil as vehicle control. Male and female offspring were examined for body weight development, external markers of prenatal androgenization and puberty onset, plasma concentrations of glucose and insulin, insulin tolerance (ITT), glucose-stimulated insulin secretion (GSIS), and the expression of peroxisome proliferator-activated receptor gamma (PPARγ) and pancreatic and duodenal homeobox 1 protein (PDX-1). Male and female rats exposed to the highest doses of DEHP and DBP exhibited increased fasting glucose levels. In rats exposed to DEHP 700 mg/kg/day we also observed a reduced glucose decay rate (Kitt) following insulin administration and decreased insulin secretion in the GSIS assay. Male offspring exposed to DEHP 700 mg/kg/day had reduced anogenital distance (AGD) on PDN 4 and delayed preputial separation at puberty, while female offspring exposed to DEHP 70 and 700 mg/kg/day and to the highest DBP dose had delayed vaginal opening. Our results suggest that maternal treatment with DEHP and DBP can induce a wide range of metabolic and reproductive alterations in offspring rats, with more pronounced effects following DEHP exposure.

Background Human exposure to phthalates and other non-persistent chemicals in developing countries is largely unknown. A preliminary analysis of urinary samples from pregnant Brazilian women revealed the presence of metabolites of Diisopentyl phthalate (DiPeP). Objectives Reliably quantify DiPeP metabolites in human urine and investigate the potential antiandrogenic activity of this phthalate in rats. Methods We initiated a pilot pregnancy cohort in Curitiba, Brazil, to examine phthalate exposure in urine samples collected in early pregnancy ( n = 50) or pooled samples from early, mid and late pregnancy ( n = 44). Our well established phthalate method was modified to include the primary DiPeP metabolite, monoisopentyl phthalate (MiPeP), and two additional secondary oxidized metabolites, 3OH-MiPeP and 4OH-MiPeP. In a parallel approach, we orally exposed pregnant rats to DiPeP or Di-n-butyl phthalate (DnBP; reference phthalate) at 0, 125, 250, and 500 mg/kg/day from gestation day 14 to 18 and measured ex vivo fetal testis testosterone production. Results We were able to detect and quantify specific DiPeP metabolites in nearly all (98%) of the early pregnancy urine samples and in all gestational pool samples with a median concentration for MiPeP of 3.65 and 3.15 μg/L, respectively, and for the two oxidized metabolites between 1.00 and 1.70 μg/L. All three urinary DiPeP metabolites were strongly correlated ( r = 0.89 to 0.99). In the rat model, the effective dose (mg/kg/day) inhibiting fetal testosterone production by 50% (ED 50 [95% confidence interval]) was 93.6 [62.9–139.3] for DiPeP which was significantly lower than for DnBP (220.3 [172.9–280.7]), highlighting the strong antiandrogenic potency of DiPeP within the spectrum of the phthalates. Conclusions We unveiled and confirmed the exposure of pregnant Brazilian women to DiPeP via specific urinary metabolites. This unexpected and ubiquitous DiPeP exposure indicates to unique DiPeP exposure sources in Brazil. These exposures spark considerable concern because DiPeP is one of the most potent antiandrogenic phthalates.

Ganciclovir (GCV) has been implicated in the development of testicular alterations. Exposure on gestational day (GD) 10 in rats induced permanent effects, including focal reduction or absence of germ cells (Sertoli cell-only tubules). Because the timing of exposure can be critical for testicular effects, we exposed rat dams to 300 mg/kg GCV (3 100 mg/kg subcutaneous injections) on GD10, 14 and 19, when germ cells have high rates of migration, proliferation and are mitotically quiescent, respectively. Males exposed to GCV in utero on GD10 and 14 were evaluated for androgenization markers, serum and fecal androgens, and testicular histomorphometry at adulthood. Double-labeling immunofluorescence for DAZL and Ki67 were used to assess gonocytes number and the proliferative activity of germ and somatic cells in fetal testes on GD15 and 20, ie, 24 h after GCV exposure. Adult rats exposed on GD14 showed delayed puberty onset, despite normal androgen levels. Also, there was a 50% reduction in testicular weight and about 30% of seminiferous tubules lacking germ cells. Effects on GD10 animals were less pronounced. In the fetal testis, the number of gonocytes was reduced by 50% in rats exposed on GD14, but normal in GD19 fetuses. GCV also reduced Sertoli cell proliferation immunolabeling in GD19 fetuses and Sertoli cell number in adults. In conclusion, GCV toxicity on germ cells seems to be linked to their proliferation rate and GD14 is a critical window in rats, when GCV exposure causes an acute massive loss of germ cells that persists until adulthood.

We examined the anogenital distance (AGD) plasticity in rats through the manipulation of the androgen environment in utero and during puberty. Dams were treated from gestation days 13–20 with vehicle, flutamide (20 mg/kg/day), di-(2-ethylhexyl) phthalate (DEHP, 750 mg/kg/day), or testosterone (1.0 mg/kg/day). After weaning, male pups were randomly assigned to one of four postnatal groups, which received the same treatments given prenatally. Sixteen treatment groups were established based on the combination of pre- and postnatal exposures. The postnatal treatments were conducted from postnatal days 23–53. In utero flutamide and DEHP exposure significantly shortened male AGD, although this effect was more pronounced in flutamide-exposed rats. Postnatal flutamide, DEHP, and testosterone induced slight but significant reductions in male AGD. Our study indicates that AGD is a stable anatomical landmark that reflects the androgen action in utero , although it can also be slightly responsive to changes in the androgen environment following pubertal exposure.

The phenomenon of teratozoospermia in felids is not fully understood. In this study, we investigated the testicular androgen:estrogen balance in domestic cats and correlated these data with epididymal sperm morphology and the degree of spermatogenic activity. During spring and summer, testes and blood samples were obtained from 37 mixed-breed domestic cats (12 to 48 mo). The epididymal sperm were harvested and evaluated for sperm counts, motility, and morphology. Distal cytoplasmic droplets were not considered a defect, and samples were considered normozoospermic if they contained more than 60% normal sperm (N = 25) or teratozoospermic if they contained less than 45% normal sperm (N = 12). The testicular and serum concentrations of testosterone (T) and 17β-estradiol (E2) were determined with an enzyme immunoassay. The gonadosomatic index and epididymal sperm numbers and motility did not differ between groups. The percentage of normal sperm was higher in normozoospermic (74.3 ± 2.0, mean ± SEM) than in teratozoospermic samples (43.1 ± 1.4). The most prevalent sperm defects in the teratozoospermic group were abnormal acrosomes (9.7 ± 2.0) and bent midpieces (12.2 ± 2.0) or tails (24.0 ± 2.7) with cytoplasmic droplets. Histomorphometric data were similar between groups, although there was a lower Leydig cell nuclear volume in teratozoospermic samples. Normozoospermic samples contained a higher percentage of haploid cells and had a higher index of total spermatogenic transformation than teratozoospermic samples. Serum concentrations of T (0.5 ± 0.1 vs. 0.8 ± 0.4 ng/mL) and E2 (9.5 ± 1.2 vs. 11.4 ± 2.3 pg/mL) and testicular T concentrations (471.6 ± 65.3 vs. 313.4 ± 57.6 ng/g) were similar between groups. However, compared with normozoospermic samples, teratozoospermic samples had higher testicular E2 concentrations (8.5 ± 3.6 vs. 5.4 ± 0.5 ng/g) and a lower T:E2 ratio (31.8 ± 4.1 vs. 87.2 ± 11.6). There were significant correlations between testicular E2 values and percentages of normal sperm (r = -0.55) as well as those with primary sperm defects (r = 0.58) or abnormal acrosomes (r = 0.64). The T:E2 ratio was also correlated with meiotic index (r = 0.45) and percentage of normal sperm (r = 0.58). In conclusion, a high testicular E2 concentration and a reduced T:E2 ratio were significantly associated with higher ratios of abnormal sperm types, suggesting that the balance between androgens and estrogens is an important endocrine component in the genesis of teratozoospermia in felids.