Dennis I. Ruggles

Effects of flaxseed and defatted flaxseed meal on reproduction and development in rats

Flaxseed, a rich source of reportedly beneficial n-3 fatty acid and phytoestrogens, has not been thoroughly tested for reproductive effects. High levels of flaxseed (FS, 20 or 40%) or defatted flaxseed meal (FLM, 13 or 26%) added to AIN-93 diet were evaluated in a two-phase study: dosed during gestation only or during gestation and maturation in a lifetime study. At cesarean section on gestation day 20, neither FS nor FLM affected fertility, body weight gain, litter size, or fetal development. FLM, but not FS, decreased gestation length. The offspring of dams allowed to litter were observed to postnatal day (PND) 21 or 90. Neither FS nor FLM affected PND 21 survival indices of F1 pups. FS (20 and 40%), but not FLM, increased the anogenital index (AGI) of F1 females at PND 21. The AGI of F1 males was not affected by either FS or FLM. FLM (13 and 26%), but not FS, delayed puberty in F1 males. Age and weight at the onset of puberty in females were not affected by FS or FLM. FS and FLM caused dose-related increases in the number of F1 females with irregular estrous cycles. During PND 21-90, F1 females fed 20% FS, 13% FLM, or 26% FLM gained more weight than the controls. FS and FLM decreased thymus/body weight and thymus/brain weight ratios in weanling F1 males and females. FS and FLM decreased liver/body weight and liver/brain weight ratios in weanling F1 females, and 26% FLM decreased the same two ratios in F1 males. In conclusion, FS did not affect fetal development but did affect indices of postnatal development such as the estrous cycle.

Developmental toxicity of sodium fluoride in rats.

Despite the chronic exposure of the US population to fluoridated drinking water since the 1940s, existing studies have been judged inadequate to determine any potential reproductive or developmental hazard. This study was conducted to determine the effects of sodium fluoride (NaF) on foetal development. Sperm-positive female rats were given 0, 10, 25, 100, 175 or 250 ppm NaF daily throughout gestation. They were dosed by drinking water to mimic human exposure to fluoridated water. No dose-related behavioural changes or maternal clinical signs were noted. Fluid consumption by females in the 175- and 250-ppm groups was significantly less than that of the control females. Because of this decreased fluid consumption, the daily amount of NaF ingested (0, 1.4, 3.9, 15.6, 24.7 and 25.1 mg/kg body weight) was less than expected at the two high levels. Feed consumption decreased significantly at 250 ppm, and body weights of pregnant females reflected feed consumption trends. The mean number of viable foetuses per female in all treated groups was similar to that of the control group. The significant decrease in the mean number of implants per litter in the 250-ppm group is probably linked to the lower mean number of corpora lutea in this group. The occurrence of in utero deaths was similar in the control and treated groups. Foetal growth (in terms of foetal body weight and crown-rump length) was not affected by NaF, despite the fact that the dams in the 250-ppm group ate significantly less feed and drank significantly less fluid. There was no dose-related increase in the number of external anomalies in foetuses due to NaF ingestion. At the doses given, NaF had no effect on the development of specific bones, including sternebrae. A significant increase was seen in the average number of foetuses with three or more skeletal variations in the 250-ppm group; the number of litters with foetuses with three or more skeletal variations was increased in the 250-ppm group also, but the increase was not significant. There was no dose-related effect of NaF on the incidence of soft tissue variations.

Developmental toxicity of sodium fluoride measured during multiple generations.

Sodium fluoride (NaF) has been used to fluoridate drinking water in the United States since the mid 1940s. Because of the lack of reliable studies on the multigeneration effects of the compound, NaF (0, 25, 100, 175 or 250 ppm in drinking water) was given to rats continuously during three generations. Parental (F0) generation rats were treated for 10 weeks and mated within groups. At gestation day 20, caesarean sections were performed and eight F0 females per group and their litters (F1) were observed for implant status, fetal weight and length, sex and morphological development. The remaining F0 females (29-32 per group) were allowed to litter. F1 offspring (36 of each sex per group) were mated within groups, and caesarean sections were performed at gestation day 20. The F1 females and their litters (F2) were observed for implant status, fetal weight and length, sex and morphological development. In addition, F2 fetuses were evaluated for internal (soft-tissue) and skeletal development. Decreased fluid consumption for F0 and F1 dams at 175 and 250 ppm was attributed to decreased palatability of the solution. No dose-related effects in feed consumption or mean body weight gain were observed in either F0 or F1 females. Numbers of corpora lutea, implants, viable fetuses and fetal morphological development were similar in all groups. No dose-related anomalies in internal organs were observed in F2 fetuses. Ossification of the hyoid bone of F2 fetuses was significantly decreased at 250 ppm. Because of the decreased ossification of the hyoid bone, 250 ppm is considered the effect level.

Rat liver clone‐9 cells in culture as a model for screening hepatotoxic potential of food‐related products: hepatotoxicity of deoxynivalenol

Deoxynivalenol (DON) is a mycotoxin food contaminant found in several cereal grains. The literature on the liver toxicity of DON in vivo is conflicting and does not clearly characterize its hepatotoxic effects. Cultured rat liver clone‐9 cells were used as a model to assess the hepatotoxic potential of DON. The cell cultures, seeded onto 96‐well plates, were treated at confluence with varying concentrations of DON (0–100 µg ml−1) for 48 h at 37 °C in 5% CO2. After the treatment period, the cells were assayed for a number of hepatotoxic endpoints that included cytotoxicity, double‐stranded DNA (ds‐DNA) content, oxidative stress and mitochondrial function. The concentration‐dependent toxicity of DON, as measured by cytotoxicity and ds‐DNA content, was observed over the entire concentration range studied beginning at 0.5 µg ml−1. DON also induced a significant concentration‐dependent increase in oxidative stress at DON concentrations starting at 10 µg ml−1. The mitochondrial function of the treated cells decreased with the increasing concentration of DON exposure, but it was not statistically different from that of the control value. Liver histopathology observed at 3, 24 and 72 h following a single intraperitoneal administration dose of DON (10 mg kg−1 BW) to adult male rats is consistent with early mild hepatotoxicity. The overall results of this study suggest that acute DON exposure has early mild cytotoxic effects on hepatocytes in vivo that are expressed as severe effects in rat liver clone‐9 cells in vitro. Published in 2008 by John Wiley & Sons, Ltd.

Multigenerational evaluation of sodium fluoride in rats

Since the mid 1940s, fluoride has been added to tap water in American communities in an effort to reduce the incidence of dental caries in the population. When the levels of fluoride in drinking water were tested and set, water was the only measurable source of fluoride for most communities. Now, adults and children ingest fluoride with foods and beverages prepared with fluoridated water, and they are exposed to fluoride-containing dental products. As a result, exposure to fluoride is greater than had been anticipated. In the early 1990s, the existing reproductive studies were reviewed in several reports and were considered to be inadequate to determine potential reproductive or developmental hazards. The effects of sodium fluoride ingestion at 0, 25, 100, 175 or 250 ppm in drinking water measured in rats throughout three generations are reported here. Feed and fluid consumption, body weights and clinical signs were recorded at regular intervals. Decreased fluid consumption observed at 175 and 250 ppm was attributed to decreased palatability and did not affect reproduction. No cumulative effects were observed in the three generations. Mating, fertility and survival indices were not affected. Organ-to-body-weight ratios and organ-to-brain weight ratios were not affected. Sodium fluoride up to 250 ppm did not affect reproduction in rats.

Effects of Fumonisin B1 in Pregnant Rats

Fumonisin B1 (FB1), the major mycotoxin from Fusarium moniliforme, has been implicated as a causative agent in several animal and human diseases. Despite animal toxicity studies and human epidemiological studies of FB1, knowledge of its reproductive effects is scarce. In this study, one of a series of proposed studies that will allow extrapolation to humans, pregnant rats were given oral doses of 0, 1.875, 3.75, 7.5 or 15 mg FB1/kg on gestation days 3 16. Caesarean sections were performed on day 17 or 20, and maternal condition, implantation efficiency, foetal viability and foetal development were measured. Dose-related decreases in overall feed consumption and body weight gain were seen, but only the feed consumption decrease at 15 mg/kg, and the decreased body weight gain at 15 mg/kg on days 0-17 were statistically significant. Foetal body weights at day 17 were similar in control and treated groups; but in day-20 foetuses, female weight and crown-rump length were significantly decreased at 15 mg/kg. FB1 was not teratogenic at the doses tested, and no dose-related effects were seen in either skeletal or soft-tissue development. In day-17 animals, maternal and foetal brain, liver and kidney tissues, and maternal serum were preserved to study the levels of sphinganine (Sa), sphingosine (So), and the Sa/So ratios. Dose-related increases were seen in Sa/So ratios in maternal livers, kidneys and serum. Sa/So ratios of maternal brains were not affected, nor were those of foetal kidneys, livers or brains.

Effects of fumonisin B1 in pregnant rats. Part 2

The developmental toxicity of purified fumonisin B1 (FB1), a mycotoxin from the common corn fungus Fusarium moniliforme, was examined in Charles River rats. Pregnant rats were dosed orally on gestation days 3-16 at 0, 6.25, 12.5, 25 or 50 mg FB1/kg body weight/day. FB1 was not teratogenic at the doses tested. At 50 mg/kg, maternal toxicity (inappetence, emaciation, lethargy, death, resorption of entire litters) and foetal toxicity (increased number of late deaths, decreased foetal body weight, decreased crown rump length, increased incidence of hydrocephalus, increased incidence of skeletal anomalies) were seen. The foetal toxicity observed at 50 mg/kg may be related to maternal toxicity. Histopathological evaluation of tissues from dams of control and all treated groups revealed dose-related toxic changes in kidney and liver tissues. Acute toxic tubular nephrosis was seen in kidneys from all treated groups. Hepatocellular cytoplasmic alteration and individual cellular necrosis of the liver was seen in the two high-dose groups. Sphinganine (Sa) and sphingosine (So) were measured in day-17 adult and foetal tissues. Dose related increases in Sa/So ratios were seen in maternal liver, kidney, serum and brain, but there was no effect on foetal liver, kidney and brain. These data suggest that FB1 does not cross the placenta and further suggest that the observed foetal toxicity is a secondary response to maternal toxicity.

Teratogenic Potential of FD&C RED NO. 3 When given by Gavage

FD&C Red No. 3 (erythrosine) is a commonly used food additive. As part of a series of studies on the potential fetal developmental effects of food colors, FD&C Red No. 3 was administered by gavage to pregnant Osborne-Mendel rats at daily dose levels of 15, 30, 100, 200, 400, or 800 mg/kg on days 0-19 of gestation. Control animals were given distilled water by gavage. On gestation day 20, the animals were euthanized and cesarean sections were performed. During the entire treatment period, feed consumption by the animals given 400 mg/kg doses was increased significantly; the increases in the animals given 30 or 800 mg/kg were of borderline significance. The only significant increase in maternal weight gain, on days 0-7 in the animals given 30 mg/kg, was considered a random occurrence. No dose-related changes were seen in maternal clinical findings, implantations, fetal viability, or fetal size (weight and length). No fetal terata were seen, and neither skeletal nor visceral development was affected. FD&C Red No. 3 was neither fetotoxic nor teratogenic at 800 mg/kg when given by gavage.

Free fatty acids profile of the fetal brain and the plasma, liver, brain and kidneys of pregnant rats treated with sodium arsenite at mid-organogenesis

Free fatty acids (FFAs) are known to be markers of cellular membrane degradation through lipid peroxidation and are substrates for the production of reactive oxygen species (ROS). Oxidative stress, due to overproduction of ROS, may facilitate cellular insult by various toxicants. The ability of the rat conceptus to respond to toxic stress may be critical for normal development. In this study, the effects of the environmental toxicant sodium arsenite (NaAsO2) on FFAs were investigated after administering a single oral dose, in water and in a lipid medium, to pregnant rats on gestational day (GD) 10, a time point at mid-organogenesis. NaAsO 2 was administered in deionized water (AsH2O) or in half and half dairy cream (AsHH) at a dose of 41 mg sodium arsenite (NaAsO 2)/kg body weight. Control animals were treated with either dairy cream (HH) or deionized water (H2O). The animals were sacrificed on GD 20. The fetal brain and the maternal liver, brain, plasma and kidneys were harvested. The FFAs were extracted and analyzed by gas chromatography. In the liver, there was an increase of myristic acid (1200%), myristoleic acid (174%), palmitic acid (47%), elaidic acid (456%), oleic acid (165%) and docosahexaenoic acid (224%) in the AsH2O group as compared to the AsHH group. Oleic acid and arachidonic acid were increased by 192% and 900%, respectively, in the AsH2O group as compared to the H 2O group, and myristic acid was decreased by 90% in the AsHH group as compared to the HH group. In the maternal brain, myristoleic acid was decreased by 91% in the AsH2O group as compared to the H2O group, and DHA increased by 148% in the AsHH group as compared to the HH group. In the fetal brain, myristic and stearic acids were decreased by 87% and 89%, respectively, in the AsH2O group as compared to the AsHH group. Myristic, stearic and arachidonic acids were increased by 411%, 265%, and 144%, respectively, in the AsHH group as compared to the HH group. There was no effect on the fatty acids concentrations in the kidney or plasma as compared to controls. This study shows that NaAsO2 produced a differential effect on the fatty acid profiles in rats. Further investigation is needed to elucidate the role of fatty acids in differential signaling and regulation by either the palmitoylation or myristoylation process of cellular functions in these target organs.

Developmental Toxicity of Orange B Given to Rats in Drinking Water

Orange B, a pyrazolone dye used to color frankfurter and sausage casings, was given in distilled drinking water to pregnant Osborne-Mendel rats throughout gestation. Assessed on the basis of fluid consumption, the dose levels of 0, 0.05, 0.1, 0.2, and 0.4% corresponded to daily Orange B consumption of 0, 67.5, 129.6, 266.6, and 532.3 mg/kg body weight, respectively. On gestation day 20, the females were euthanized and cesarean sections were performed. Throughout gestation, the treated animals consumed less fluid than did the controls, but the decreases were not dose-related. Feed consumption and maternal weight gain were not affected. No dose-related changes were seen in maternal clinical findings, implantations, fetal viability, or fetal size (weight and length). No compound-related effects were seen in sternebral development. Ossification of the interparietal bones was reduced at some dose levels, but the decreases were considered random because of absence of dose response. No dose-related effect was seen in the incidence of skeletal variations in fetuses or in the number of litters containing fetuses with skeletal variations. Skeletal development, as measured by the average number of ossified vertebrae, was similar in all groups. Soft-tissue development was not affected by dose levels of 0.05 to 0.2%. In animals treated with 0.4% Orange B, significant increases were seen in the incidence of hydroureters (severe and moderate), in the average numbers of fetuses with at least one and at least two soft-tissue variations per litter, and in the percentage of litters containing fetuses with at least two soft-tissue variations.