Utilization of a model hepatotoxic compound, diglycolic acid, to evaluate liver Organ-Chip performance and in vitro to in vivo concordance.

Microphysiological systems (MPS) are emerging as potentially predictive models for drug safety and toxicity assessment. To assess the utility of these systems, the Food and Drug Administration partnered with Emulate to evaluate the Human Liver Organ-Chip in a regulatory setting. Diglycolic acid (DGA), a known hepatotoxin, was evaluated in the Liver-Chip and compared to a multi-well plate format to assess the Liver-Chip's capabilities, limitations, overall performance, and concordance with other in vivo and in vitro studies. Cryopreserved primary human hepatocytes were exposed to DGA from 1 to 20 mM in Liver-Chips or traditional multi-well plates. We found that 10 mM or 20 mM of DGA was severely cytotoxic in both platforms, while 5 mM was mildly cytotoxic in Liver-Chips. Additionally, some hepatocyte functions were reduced with 5 mM DGA in Liver-Chips and 1 mM in well plates. Individual well effects were greater or occurred sooner than in the Liver-Chips. Examination of the performance of the Liver-Chip showed that variability was low for biochemical endpoints, but higher for imaging endpoints. Sensitivity and specificity were high. Only 3-4 Liver-Chips were necessary to detect an effect depending on the endpoint and effect size. The specifics of the experiment are found herein.

C. elegans Development and Activity Test detects mammalian developmental neurotoxins.

Due to the high cost and long duration of traditional testing methods for developmental neurotoxicity (DNT), only a small fraction of chemicals that humans are exposed to have been assessed for DNT activity. In order to ensure public safety, human-predictive methods for DNT detection that are faster and less resource intensive are urgently required. Using Caenorhabditis elegans, a novel worm Development and Activity test (wDAT) has been designed that uses a relatively inexpensive small-animal activity tracker and takes less than 4 days to complete. The wDAT was able to detect both developmental delay and hyperactivity for arsenic, lead, and mercury, heavy metals that are known human developmental neurotoxins and have been associated with hyperactivity in children. Lithium was also tested as a control developmental toxin that is not considered a mammalian neurotoxin. With the wDAT, lithium induced developmental delay but not hyperactivity. This initial assessment of a new assay for DNT detection indicates that the wDAT has potential for detecting at least some types of mammalian developmental neurotoxins. A planned 20-compound validation study will clarify the utility of the wDAT for predicitive toxicology.

Diglycolic acid induces HepG2/C3A liver cell toxicity in vitro.

Carboxymethyl starches are added to food products for thickening or tablet binding/filling purposes. Although they lack toxicity, their synthesis creates the chemical byproduct diglycolic acid (DGA), which is difficult to eliminate and whose toxicity is in question. A rare case of an accidental direct exposure to extremely high concentrations of DGA in a person revealed that DGA has the potential to be toxic to several organs, with the kidneys and liver being the most affected organs. Given that DGA is present in our food supply as a chemical byproduct of carboxymethyl starch food additives, we sought to perform in vitro testing of its potential hepatotoxicity to help complement a recent in vivo rat acute dose-response study that also tested for the potential hepatotoxic effects of daily DGA ingestion by oral gavage over a period of 28 days. Using the HepG2/C3A cellular in vitro model, we tested how escalating doses of DGA exposure over 24 h could induce hepatotoxicity. Both in vitro and in vivo testing systems revealed that DGA is indeed a hepatotoxin once a certain exposure threshold is reached. The concordance of these models highlights the utility of in vitro testing to support and help predict in vivo findings.

Comparison of diglycolic acid exposure to human proximal tubule cells in vitro and rat kidneys in vivo.

Diglycolic acid (DGA) is present in trace amounts in our food supply and is classified as an indirect food additive linked with the primary GRAS food additive carboxymethyl cellulose (CMC). Carboxymethyl starches are used as a filler/binder excipient in dietary supplement tablets and a thickening ingredient in many other processed foods. We sought to utilize the human proximal tubule HK-2 cell line as an in vitro cellular model system to evaluate its acute nephrotoxicity of DGA. We found that DGA was indeed toxic to HK-2 cells in all in vitro assays in our study, including a highly sensitive Luminex assay that measures levels of an in vitro biomarker of kidney-specific toxicity, Kidney Injury Molecule 1 (KIM-1). Interestingly, in vitro KIM-1 levels also correlated with in vivo KIM-1 levels in urine collected from rats treated with DGA by daily oral gavage. The use of in vitro and in vivo models towards understanding the effectiveness of an established in vitro system to predict in vivo outcomes would be particularly useful in rapidly screening compounds that are suspected to be unsafe to consumers. The merit of the HK-2 cell model in predicting human toxicity and accelerating the process of food toxicant screening would be especially important for regulatory purposes. Overall, our study not only revealed the value of HK-2 in vitro cell model for nephrotoxicity evaluation, but also uncovered some of the mechanistic aspects of the human proximal tubule injury that DGA may cause.

Assessing the effect of oral exposure to Paenibacillus alvei, a potential biocontrol agent, in male, non-pregnant, pregnant animals and the developing rat fetus.

Paenibacillus alvei, a naturally occurring soil microorganism, may be used in the control and/or elimination of human/animal pathogens present on/within produce commodities associated with human consumption. The safety of oral exposure to P. alvei in male, nulliparous females, the pregnant dam and developing fetus was assessed. Adult male and female rats received a single oral dose (gavage) of P. alvei and tissues were collected at post exposure days 0, 3 and 14. To evaluate the effect of the test organism on fetal development, sperm positive female rats received the test organism every 3 days thereafter throughout gestation. As human exposure would be no more than 1 × 103 CFU/ml the following dose levels were evaluated in both study phases: 0 CFU/ml tryptic soy broth (negative control); 1 × 108 CFU/ml; 1 × 104 CFU/ml or 1 × 102 CFU/ml. Neither sex specific dose-related toxic effects (feed or fluid consumption, body weight gain, and histopathology) nor developmental/reproductive effects including the number of implantations, fetal viability, fetal weight, fetal length and effects on ossification centers were observed. The test organism did not cross the placenta and was not found in the amniotic fluid.

28-day repeated dose response study of diglycolic acid: Renal and hepatic effects.

The acute oral toxicity of diglycolic acid (DGA) was evaluated. Groups of female rats (n = 8 rats/group) received 28 consecutive daily single doses of 0.3, 1.0, 3.0, 10.0, 30.0, 100.0 or 300.0 mg DGA/kg body weight by gastric intubation. One group of animals served as vehicle control. Tissues and blood serum were collected at necropsy on day 29. Select organs were weighed and fixed in formalin for histopathological analysis. Animals from the 300 mg/kg bw dose group were removed from the study after 5 consecutive days of treatment as a consequence of adverse treatment related effects. The animals in the remaining treatment groups survived the exposure period. No adverse clinical signs were observed throughout the exposure period in the surviving animals. No significant differences from controls were observed for feed and fluid consumption or body weight gain in the surviving animals. Lesions were observed in the kidneys, liver, stomach, intestine, thymus, spleen and bone marrow in rats from the 300 mg/kg dose group and signs of renal tubular regeneration were observed only in the 100 mg/kg dose group. These results suggest that high levels of pure DGA would need to be consumed before renal and other forms of organ toxicity are observed.

Silver acetate exposure: Effects on reproduction and post natal development.

Effects of oral silver acetate exposure were assessed in P generation and F generation post-natal day 26 rats. Male and female Sprague Dawley rats (n = 20 each) were exposed to silver acetate at 0.4, 4.0 or 40.0 mg/kg bw in their drinking water for 10 weeks prior to and during mating. Females were exposed to silver acetate throughout gestation and lactation. Clinical signs, body weight, feed and fluid consumption were recorded regularly. Decreased mean daily fluid consumption was observed in male and female animals during the 10 week pre mating period and during gestation in the 40 mg/kg bw dose group. Decreased fertility was observed in the 40 mg/kg bw dose group. Decreased feed consumption was observed across all dose groups and decreased mean daily fluid consumption was observed in the 4.0 mg/kg dose group during lactation. Decreased implant numbers, mean numbers of pups born/litter and numbers of live pups born/litter was observed in the 40 mg/kg bw dose group. Pup weight was reduced on lactation days 0, 4 and 7 (males) and 4, 7 and 21 (females) in the 4.0 mg/kg bw dose group and in males at lactation day 21 (40 mg/kg bw dose group). Runting was observed in males (Lactation Day; LD 4) and female (LD 4 and 7) animals in the 4.0 mg/kg bw dose group. Reduced postnatal-day 26 pup weight was observed in male pups in the 40 mg/kg bw dose group and female pups in the 4.0 mg/kg bw dose group.

Effects of maternal silver acetate exposure on immune biomarkers in a rodent model.

Male and female rats (26-day old) were exposed to 0.0, 0.4, 4 or 40 mg/kg body weight silver acetate (AgAc) in drinking water for 10 weeks prior to and during mating. Sperm positive females remained within their dose groups and were exposed to AgAc during gestation and lactation. Splenic and thymic lymphocyte subsets from F1 generation PD (postnatal day) 4 and 26 pups were assessed by flow cytometry for changes in phenotypic markers. Spleens from PD4 pups had lower percentages of CD8+ lymphocytes in 4 and 40 mg/kg AgAc exposed groups and reduced Concanavalin A (Con A) response at all AgAc exposure groups. Splenic maturation increased in PD26 pups compared to PD4 pups. Con A and lipopolysaccharide (LPS) mediated splenic responses were lower in PD26 pups exposed to 40 mg/kg AgAc. Changes in PD 26 pup splenocyte phenotypic markers included lower TCR + cells at 4 and 40 mg/kg AgAc exposure and higher B cell population in the 40 mg/kg AgAc. PD26 pup splenic natural killer cell (NK) activity was higher in the 0.4 AgAc group and unchanged in 4 and 40 mg/kg AgAc groups. In conclusion, maternal exposure to AgAc had a significant impact on rat splenic development during the early lactation period.

Toxicogenomic study in rat thymus of F1 generation offspring following maternal exposure to silver ion.

Male and female rats (26-day-old) were exposed to 0.0, 0.4, 4 or 40 mg/kg body weight silver acetate (AgAc) in drinking water for 10 weeks prior to and during mating. Sperm-positive females remained within their dose groups and were exposed to silver acetate during gestation and lactation. At postnatal day 26, the effect of silver ions on the developing F1 generation rat thymus was evaluated at the transcriptional level using whole-genome microarrays. Gene expression profiling analyses identified a dozen differentially expressed genes (DEGs) in each dose group using a loose criterion of fold change (FC) >1.5 and unadjusted p < 0.05, regardless of whether the analysis was conducted within each gender group or with both gender groups combined. No dose-dependent effect was observed on the number of DEGs. In addition, none of these genes had a false discovery rate (FDR) <0.05 after correction for multiple testing. These results in combination with the observation that thymus-to-body-weight ratios were not affected and no histopathological abnormalities were identified indicate that in utero exposure to silver ions up to 26.0 mg/kg (equivalent to 40.0 mg/kg silver acetate) did not have an adverse effect on the developing thymus.

Reproductive toxicity in rats with crystal nephropathy following high doses of oral melamine or cyanuric acid.

The industrial chemical melamine was used in 2007 and 2008 to raise the apparent protein content in pet feed and watered down milk, respectively. Because humans may be exposed to melamine via several different routes into the human diet as well as deliberate contamination, this study was designed to characterize the effect of high dose melamine or cyanuric acid oral exposure on the pregnant animal and developing fetus, including placental transfer. Clear rectangular crystals formed following a single triazine exposure which is a different morphology from the golden spherulites caused by combined exposure or the calculi formed when melamine combines with endogenous uric acid. Crystal nephropathy, regardless of cause, induces renal failure which in turn has reproductive sequelae. Specifically, melamine alone-treated dams had increased numbers of early and late fetal deaths compared to controls or cyanuric acid-treated dams. As melamine was found in the amniotic fluid, this study confirms transfer of melamine from mammalian mother to fetus and our study provides evidence that cyanuric acid also appears in the amniotic fluid if mothers are exposed to high doses.

Bioactivity of nanosilver in Caenorhabditis elegans: Effects of size, coat, and shape.

The in vivo toxicity to eukaryotes of nanosilver (AgNP) spheres and plates in two sizes each was assessed using the simple model organism Caenorhabditis elegans. For each shape, smaller AgNP size correlated with higher toxicity, as indicated by reduced larval growth. Smaller size also correlated with significant increases in silver uptake for silver nanospheres. Citrate coated silver spheres of 20 nm diameter induced an innate immune response that increased or held steady over 24 h, while regulation of genes involved in metal metabolism peaked at 4 h and subsequently decreased. For AgNP spheres, coating altered bioactivity, with a toxicity ranking of polyethylene glycol (PEG) > polyvinylpyrrolidone (PVP) ≅ branched polyethyleneimine (BPEI) > citrate, but silver uptake ranking of PEG > PVP > citrate > BPEI. Our findings in C. elegans correlate well with findings in rodents for AgNP size vs. uptake and toxicity, as well as for induction of immune effectors, while using methods that are faster and far less expensive, supporting the use of C. elegans as an alternative model for early toxicity screening.

Nanosilver suppresses growth and induces oxidative damage to DNA in Caenorhabditis elegans.

Studies on the effects of nanomaterial exposure in mammals are limited, and new methods for rapid risk assessment of nanomaterials are urgently required. The utility of Caenorhabditis elegans cultured in axenic liquid media was evaluated as an alternative in vivo model for the purpose of screening nanomaterials for toxic effects. Spherical silver nanoparticles of 10 nm diameter (10nmAg) were used as a test material, and ionic silver from silver acetate as a positive control. Silver uptake and localization, larval growth, morphology and DNA damage were utilized as endpoints for toxicity evaluation. Confocal reflection analysis indicated that 10nmAg localized to the lumen and tissues of the digestive tract of C. elegans. 10nmAg at 10 µg ml(-1) reduced the growth of C. elegans larvae, and induced oxidative damage to DNA as measured by 8-OH guanine levels. Consistent with previously published studies using mammalian models, ionic silver suppressed growth in C. elegans larvae to a greater extent than 10nmAg. Our data suggest that medium-throughput growth screening and DNA damage analysis along with morphology assessments in C. elegans could together provide powerful tools for rapid toxicity screening of nanomaterials.

Performance of urinary and gene expression biomarkers in detecting the nephrotoxic effects of melamine and cyanuric acid following diverse scenarios of co-exposure.

Although standard nephrotoxicity assessments primarily detect impaired renal function, KIM-1, clusterin, NGAL, osteopontin and TIMP-1 were recently identified biomarkers proposed to indicate earlier perturbations in renal integrity. The recent adulteration of infant and pet food with melamine (MEL) and structurally-related compounds revealed that co-ingestion of MEL and cyanuric acid (CYA) could form melamine-cyanurate crystals which obstruct renal tubules and induce acute renal failure. This study concurrently evaluated the ability of multiplexed urinary biomarker immunoassays and biomarker gene expression analysis to detect nephrotoxicity in F344 rats co-administered 60ppm each of MEL and CYA in feed or via gavage for 28days. The biomarkers were also evaluated for the ability to differentiate the effects of the compounds when co-administered using diverse dosing schedules (i.e., consecutive vs. staggered gavage) and dosing matrixes (i.e., feed vs. gavage). Our results illustrate the ability of both methods to detect and differentiate the severity of adverse effects in the staggered and consecutive gavage groups at much lower doses than previously observed in animals co-exposed to the compounds in feed. We also demonstrate that these urinary biomarkers outperform traditional diagnostic methods and represent a powerful, non-invasive indicator of chemical-induced nephrotoxicity prior to the onset of renal dysfunction.

Timing and route of exposure affects crystal formation in melamine and cyanuric exposed male and female rats: gavage vs. feeding.

Effects of the dosing matrix and timing on the onset of renal crystal formation were evaluated in male and non-pregnant female rats (Fisher 344) exposed to both melamine (MEL) and cyanuric acid (CYA) for 28 days. Rats were fed ground feed containing 60 ppm MEL and 60 ppm CYA, (5 mg/kg bw/day equivalent), or exposed via oral gavage to carboxymethylcellulose containing 5 mg/kg bw MEL followed by 5 mg/kg bw CYA either consecutively (<1 min apart) or delayed 45 min after MEL. Staggered gavage exposure to MEL/CYA caused extensive renal crystal formation as compared to when the two compounds were administered consecutively or in feed. Treatment related effects included reduced weight gain, feed consumption, and testicular weight and increased kidney weight, water consumption and urine output. Animals from the staggered MEL/CYA gavage exposure group became ill and were removed after 9 days of exposure. Approximately 1 week after the initiation of exposure microscopic urinalysis revealed MEL/CYA crystals in both groups of gavaged animals but not in the MEL/CYA feed treatment groups. Urinary crystals were smaller (10 µm) in animals consecutively gavaged. In contrast the urinary crystals were larger (20-40 µm) and frequently clumped in the animals in the staggered gavage group.

Toxicity ranking of heavy metals with screening method using adult Caenorhabditis elegans and propidium iodide replicates toxicity ranking in rat.

The utility of any model system for toxicity screening depends on the level of correlation between test responses and toxic reactions in humans. Assays in Caenorhabditis elegans can be fast and inexpensive, however few studies have been done comparing toxic responses in this easily cultured nematode with data on mammalian toxicity. Here we report that a screening assay for acute toxicity, using adult C. elegans grown in axenic liquid culture, replicated LD50 toxicity ranking in rat for five metals. This assay utilized the COPAS Biosort and propidium iodide (PI) as a fluorescent indicator of morbidity and mortality after 30-h exposures. We found that chronic toxicity assays of 2-week treatment duration, followed by analysis of PI induced red fluorescence levels, produced less consistent results than the acute assays. However, other chronic toxicity endpoints were compound and concentration specific, including changes in vulval and gonadal morphology, intestinal thickness and integrity, and the presence of retained internal eggs in post-reproductive animals. Some of these endpoints reflect similar findings in mammals, indicating that measurements of morbidity and mortality in conjunction with morphology analyses in C. elegans may have the potential to predict mammalian toxic responses.

A method to rank order water soluble compounds according to their toxicity using Caenorhabditis elegans, a Complex Object Parametric Analyzer and Sorter, and axenic liquid media.

Complex Object Parametric Analyzer and Sorter (COPAS) parameters Time of Flight (TOF) and Extinction (EXT) were utilized to assess growth and development in Caenorhabditis elegans exposed to (in order of decreasing toxicity) sodium arsenite, sodium fluoride, caffeine, valproic acid, sodium borate or DMSO in C. elegans Habitation Medium (CeHM) for 72h. Using multivariate statistical modeling and unique sub sampling procedures mean p-value ratios were calculated for each compound. Comparison of mean p-value ratios and/or the percent change in mean-p value ratios to controls were utilized to assess test compound toxicity. Using this assay 5 of the 6 compounds tested (83.3%) were correctly ranked according to their toxicity based on oral rat LD50 data. Test compounds were ranked from most toxic to least toxic as follows: sodium arsenite, sodium fluoride, sodium borate, valproic acid, caffeine and DMSO. Sodium borate was found to be more toxic than caffeine and valproic acid in this bioassay. This study suggests that axenic liquid culture may be used to expose large numbers of nematodes to water soluble toxicants and the COPAS parameters TOF and EXT may be used as functional biomarkers to assess a toxin's effect on growth and development in C. elegans.

Effects of zearalenone on in utero development in rats.

Zearalenone (ZE), an estrogenic mycotoxin produced by Fusarium graminearum or F. roseum, is one of the most common contaminants of cereal grains world-wide. The objective of this study was to determine the effects of ZE on in utero development of rats. Pregnant female Charles River Sprague-Dawley rats were gavaged once daily with ZE (in corn oil) at doses of 0, 1, 2, 4, or 8 mg/kg body weight on gestation days (GD) 6-19. All females survived to cesarean section on GD 20. At cesarean section, reproductive and developmental parameters were measured and blood was taken for hormone analysis. Dose-related decreases were seen in maternal feed consumption and body weight gain in all treated groups. Delayed fetal development was linked to maternal toxicity. Fetal body weight was significantly decreased in both sexes in all treated groups. ZE retarded skeletal ossification at 4 and 8 mg/kg. Fetal anogenital index (anogenital distance normalized for body weight) was increased in all treated groups, indicating an androgenic effect of ZE during fetal development. Fetal viability was significantly decreased at 8 mg/kg; significant decreases were observed in number of viable fetuses, and number of litters totally resorbed. At 4 and 8 mg/kg, maternal liver-body weight ratios were significantly increased and organ-brain weight ratios for weights of liver, heart, spleen, kidneys, and ovaries were significantly decreased. Gonadotropins (LH, FSH, and prolactin) and sex steroids (progesterone and estradiol) were analyzed from the blood serum obtained at cesarean section. LH in the 0, 1, 2, and 4 mg/kg groups showed minimal variation, and slightly increased at 8 mg/kg. FSH was decreased in the 1, 2, and 4 mg/kg groups, but the level at 8 mg/kg was slightly higher than the control level. Prolactin level was not affected at 1 mg/kg, slightly increased at 2 and 4 mg/kg, and significantly increased at 8 mg/kg. Progesterone was decreased at 2, 4, and 8 mg/kg and the decreases were significant at 2 and 4 mg/kg. Estradiol level was not affected at 1mg/kg, but dose-related decreases were observed at 2, 4, and 8 mg/kg. Only the 8 mg/kg level of estradiol was significantly decreased. In summary, ZE was maternally toxic and fetotoxic but not teratogenic. The increased anogenital distance observed in male and female fetuses was considered a hormonal change rather than a teratologic response. The increased anogenital distance indicated an androgenic effect. Based on the dose-related maternal and fetal toxicity in all treated groups, the NOEL for reproductive and teratogenic effects was less than 1 mg/kg.

Effects of aminopentol on in utero development in rats.

UNLABELLED: Aminopentol (AP1), the backbone and main hydrolysis product of the mycotoxin fumonisin B1 (FB1), is present in corn-based foods which are consumed daily as a substantial part of the diet in some areas of the world. The toxicity of FB1 has been attributed to altered sphingolipid metabolism, but the toxicity of AP1 is less certain. Epidemiological correlations and in vitro studies have suggested that AP1 can increase neural tube defects (NTDs), but no in vivo developmental study of AP1 was done prior to this study. AP1 was given once daily to rats by gavage on gestation days (GD) 3-16 at doses of 0, 15, 30, 60, or 120 mg/kg. Reproductive and developmental parameters were measured at GD 17, one day after the last dose, and on GD 20. In addition, on GD 17, maternal and fetal tissues were analyzed for sphingolipid content. CONCLUSIONS: AP1 reduced dam body weight gain, but was less toxic than FB1. AP1 was not teratogenic, did not affect tissue sphingolipid ratios, did not alter reproduction or development of fetuses, and produced no dose-related histopathological effects in dams.

Effects of deoxynivalenol (DON, vomitoxin) on in utero development in rats.

Deoxynivalenol (DON, vomitoxin), is one of the most common contaminants of cereal grains world-wide. The effects of DON on fetal development were assessed in Charles River Sprague-Dawley rats. Pregnant female rats were gavaged once daily with DON at doses of 0, 0.5, 1, 2.5, or 5 mg/kg body weight on gestation days (GD) 6-19. At cesarean section on GD 20, reproductive and developmental parameters were measured. All females survived to cesarean section. DON caused a dose-related increase in excessive salivation by the pregnant females, a reaction probably linked to the lack of emetic reflex in rats. At 5 mg/kg, feed consumption and mean body weight gain were significantly decreased throughout gestation, mean weight gain (carcass weight), and gravid uterine weight were significantly reduced, 52% of litters (12/23) were totally resorbed, the average number of early and late deaths per litter was significantly increased, average fetal body weight and crown-rump length were significantly decreased, the incidence of runts was significantly increased, and the ossification of fetal sternebrae, centra, dorsal arches, vertebrae, metatarsals, and metacarpals was significantly decreased. At 2.5 mg/kg, DON significantly decreased average fetal body weight, crown-rump length, and vertebral ossification. These effects may be secondary to maternal toxicity and the reduced size of the fetuses. The incidence of misaligned and fused sternebrae was significantly increased at 5.0 mg/kg. No adverse developmental effects were observed at 0.5 and 1.0 mg/kg. Dose-related increases in maternal liver weight-to-body weight ratios were observed in all treated groups (significant at 1, 2.5, and 5 mg/kg). The weight changes were correlated with dose-related cytoplasmic alterations of hepatocytes. The NOEL for maternal toxicity for this study is 0.5 mg/kg based on the dose-related increase in liver-body weight ratio at 1 mg/kg. The NOEL for fetal toxicity is 1 mg/kg based on the general reduction in fetal development at 2.5 and 5 mg/kg. DON is considered a teratogen at 5 mg/kg day in Sprague-Dawley rats based on the anomalous development of the sternebrae.

Maternal exposure to androstenedione does not induce developmental toxicity in the rat.

Thirty-day old female rats received corn oil or androstenedione (in corn oil) at one of four concentrations (5.0, 10.0, 30.0 or 60.0 mg/kg body weight) by gavage for two weeks prior to mating, during the mating period and until gestation day (GD) 19. Caesarean sections were performed on GD 20. No dose related changes were observed in serum androstenedione, estradiol, LH, FSH, testosterone or progesterone. A statistically significant decrease in estrous cycle length was observed in the 60.0 mg/kg dose group only. Feed and fluid consumption, mean body weight gain, organ weight and fetal parameters were not affected by androstenedione treatment. At the doses given, androstenedione had no specific effect on the development of individual bones or soft tissues.