Two-generation Reproductive Toxicity Research Articles

The conduct of a two-generation reproductive toxicity study via dermal exposure in the Sprague-Dawley rat—a case study with KBR 3023 (a prospective insect repellent)

KBR 3023, 1-(1-methyl-propoxycarbonyl)-2-(2-hydroxyethyl)-piperidine, a prospective insect repellent being developed by the Bayer Corporation, was evaluated for reproductive toxicity in the Sprague-Dawley rat. As the intended human use of the test compound is topical, the test system was also exposed to the compound via the dermal route. Specifically, the adult rats (P generation) were fitted with Elizabethan collars, to reduce the likelihood of oral ingestion, and dermally administered either 0, 50, 100, or 200 mg KBR 3023/kg body weight throughout the study (5 d/week) beginning at the onset of the 10-week premating period and continuing through the mating, gestation, and lactation phases. Clinical signs and changes in body weight and food consumption were assessed throughout the study. All adults and neonates underwent a gross necropsy examination. Tissues retained for microscopic examination from all adult animals included the kidney, liver, pituitary, reproductive organs, and samples of skin from the shaved dose site. In addition to the parameters noted above, the animals were evaluated for the effect of the test compound on estrous cycling, mating, fertility, gestation length, litter size, pup sex ratio, and pup viability. There were no test compound-related clinical signs or effects on body weight or food consumption observed in either the adults or the pups during any phase of the study. There were no compound-related effects on any reproductive or litter parameters. Dermal findings at the dose site (acanthosis and hyperkeratosis) were noted in both generations. Other than the dermal findings, no compound-related necropsy findings were seen in either the adults or the pups. No compound-related histopathologic findings were noted in the reproductive tissues of either the males or females. Based on these results, KBR 3023, administered as described in this study at dose levels as high as 200 mg/kg body weight (the physical limit of dermal application for this compound), did not demonstrate any reproductive toxicity.

Two-generation reproductive toxicity study of plant stanol esters in rats.

Plant stanol esters are intended for use as an ingredient in food to reduce the absorption of cholesterol from the gastrointestinal tract. Consumption of plant stanol esters has a demonstrated diet-derived public health benefit, as shown by numerous clinical studies. Plant stanol esters are ring-saturated analogs of common dietary sterols that are transesterified with fatty acids from vegetable oils such as canola oil. The reproductive and developmental toxicity of plant stanol esters was investigated in male and female Wistar rats during F0 and F1 generations using dietary concentrations of 1.75, 4.38, and 8.76% stanol esters (equivalent to 1, 2.5, and 5% total stanols). No adverse treatment-related effects were noted on reproductive performance of male or female rats in any dose group. Increased food consumption was observed in high-dose F0 generation males throughout the entire premating period and in F1 males at specific time periods during the premating period. This increase in food consumption was also observed in F0 generation females (mid- and high-dose groups) and F1 generation females (low-, mid-, and high-dose groups) at specific time periods throughout the 10-week premating period. At different intervals throughout the gestation and lactation periods, increased food consumption was observed in F0 generation females of the mid- and high-dose groups, while increased food consumption was noted in F1 generation females of the mid- and high-dose groups during gestation, but not during lactation. Such increases in food consumption are expected as a result of the animals' attempt to compensate for the reduced caloric value of the test diet compared to controls. No adverse developmental effects were noted in F1 or F2 pups of the low- and mid-dose groups based on evaluation of the following parameters: litter size, pup mortality, pups weights, and sex ratio. However, a treatment-related effect on body weight and body weight change was observed in both F1 and F2 male and female pups of the high-dose group, particularly during the latter stages of lactation (postnatal days 14 and 21) in F1 pups, and during the majority of the lactation period (postnatal days 4-21). Lower body weight in the high-dose pups is attributed to a reduction in the caloric value of the test diet compared to control. The pups, unlike adult animals, are particularly sensitive to reductions in caloric value of feed since they are in a rapid growth phase of their development. It is likely that they could not increase their food consumption enough to adequately meet their caloric and nutritional needs. In conclusion, dietary concentrations of up to 4.38% plant stanol esters (equivalent to 2.5% total stanols in the diet) are not associated with adverse effects on reproduction, pup mortality, pup body weight, or pup body weight change.

Chemical warfare agents: estimating oral reference doses.

Health risk assessments for sites contaminated with chemical warfare agents require a comparison of the potential levels of exposure with a characterization of the toxic potency of each chemical. For noncancer health effects, toxic potency is expressed in terms of Reference Doses (RfD). A RfD is a daily exposure level or dose (usually expressed in units of milligrams of chemical per kilogram body weight per day) for the human population, including sensitive subpopulations, that is likely to be without an appreciable risk of deleterious effects. A daily exposure at or below the RfD is not likely to be associated with health risks, but as the amount of chemical that an individual is exposed to increases above the RfD, the probability that an adverse effect will occur also increases. A RfD is derived by first examining the available human or animal toxicity data to identify a dose or exposure that corresponds to a no-observed-adverse-effect level (NOAEL) or a lowest-observed-adverse-effect level (LOAEL). The NOAEL is the exposure level at which there are no statistically or biologically significant increases in frequency or severity of adverse effects between the exposed population and its appropriate control. Effects may be produced at this level, but they are not considered to be adverse if they do not result in functional impairment or pathological lesions that affect the performance of the whole organism or which reduce an organism's ability to cope with additional challenge. The LOAEL is the lowest exposure level at which there are statistically or biologically significant increases in frequency or severity of adverse effects between the exposed population and its appropriate control. If only a LOAEL is identified by the toxicity data, a NOAEL is estimated by dividing the LOAEL by a factor no greater than 10. This extrapolation factor of 10 or less is termed the LOAEL-to-NOAEL Uncertainty Factor (UFL). The NOAEL is also adjusted by the application of other Uncertainty Factors, including (1) a UFH < or = 10 to ensure that the resulting RfD protects segments of the human population that may be more sensitive to the chemical than the average person; (2) a UFA < or = 10 to extrapolate from the experimental animal species to humans; (3) a UFS < or = 10 to extrapolate from an experimental subchronic exposure study to a potential chronic exposure; and (4) a UFD < or = 10 to ensure that the resulting RfD is protective for all possible adverse effects, particularly those that may not have been adequately evaluated in the available studies. A Modifying Factor (MF), based on a qualitative professional assessment of the data, may also be used to account for other factors (e.g., deficiencies in the critical study) that are not adequately covered by the standard Uncertainty Factors. 1. Agent HD (Sulfur Mustard). RfDe = 7 x 10(-6) mg kg-1 d-1. A LOAEL was identified in a two-generation reproductive toxicity study conducted in rats. A total uncertainty factor of 3000 was applied to account for protection of sensitive subpopulations (10), animal-to-human extrapolation (10), LOAEL-to-NOAEL extrapolation (3), and extrapolation from a subchronic to chronic exposure (10). A LOAEL-to-NOAEL UF of 3, instead of the default value of 10, was used because the critical effect (stomach lesions) was considered to be "mild" in severity and may have been enhanced by the vehicle used (sesame oil in which sulfur mustard is fully soluble) and the route of administration (gavage), which is more likely to result in localized irritant effects. The key study did identify a toxic effect that is consistent with the vesicant properties of sulfur mustard. In none of the other available studies was there any indication of a different effect occurring at a lower exposure level.

Acrylic acid: two-generation reproduction toxicity study in Wistar rats with continuous administration in the drinking water

In a two-generation reproduction toxicity study, groups of 25 male and 25 female Wistar rats (for both F 0 and F 1 generations) received acrylic acid (AA) in the drinking water at concentrations of 0 (control), 500, 2500 and 5000 ppm for at least 70 days prior to mating, through mating, gestation, lactation and to weaning. The study continued through to weaning of the F 2 offspring at 21 days of age. Achieved intakes of AA for the F 0 and F 1 parents during premating ranged from 46 (500 ppm) to 502 (5000 ppm) mg/kg/day. AA had no adverse effects on fertility and reproductive performance of the parent rats at doses up to 5000 ppm. General systemic toxicity was apparent with reduced body weights, food and water consumption in F 0 parents at 5000 ppm and in F 1 parents at 2500 and 5000 ppm; the only treatment-related pathological finding was a minimal hyperkeratosis of the limiting ridge of the forestomach with a minimal oedema of the submucosa of the glandular stomach in both parental generations at 5000 ppm. Dose-related signs of developmental toxicity were detected in F 1 and F 2 pups at 2500 and 5000 ppm in the form of retarded growth and some delay in the eye/auditory canal opening in F 2 pups, but there was no evidence that AA had an adverse influence on pup morphology. Thus, the no-observed-adverse-effect level (NOAEL) is 5000 ppm for fertility and reproductive performance of the parents, 2500 ppm (F 0 parents) or 500 ppm (F 1 parents) for general systemic toxicity and 500 ppm for developmental toxicity.

Two-generation reproductive toxicity study of methyl tertiary-butyl ether (MTBE) in rats.

A two-generation reproductive toxicity study of methyl tertiary-butyl ether (MTBE) was conducted in Sprague-Dawley rats. Twenty-five rats of each sex (F0) were exposed by inhalation to 0, 400, 3000 or 8000 ppm MTBE vapor, 6 h a day for 10 weeks prior to mating. Parental animals were then mated within groups for up to 3 weeks. Parental females were exposed during mating, gestation and lactation (starting on day 5); parental males were exposed during mating through delivery of their last litter sired. The F1 adults were selected from the F1 litters and were exposed beginning on postnatal day 28 for at least 8 weeks before mating to produce F2 litters. During exposures to 3000 and 8000 ppm MTBE, group observations included hypoactivity and lack of startle reflex in parental animals from both generations. Parental animals at 8000 ppm were also ataxic. During the pre-mating period, body weights of the 8000 ppm males from both generations and the F1 females were significantly reduced compared to control animals. Transient body weight reduction was also observed in the 3000 ppm F1 males and females during the pre-mating period. Lactational body weights were increased in the 8000 ppm females from both generations. In the F1 generation, increased liver weights were noted in the 3000 and 8000 ppm animals for both sexes, although histopathological examination revealed no treatment-related effects. There were no treatment-related reproductive effects noted in any of the parameters measured in this study. Offspring survival was equivalent among treated and control groups from both generations, and there were no remarkable post-mortem findings. There was, however, a significant increase in dead F2 pups in the 8000 ppm group on postnatal day 4. The F1 litters at 3000 and 8000 ppm had lowered body weights from postnatal days 14-21 and 14-28, respectively. The F2 generation of pups at 3000 and 8000 ppm also exhibited lowered body weights from postnatal days 14-28 and 7-28, respectively. Body weight gains in both the F1 and F2 litters were also reduced for the corresponding time intervals. Thus, exposure to MTBE vapor produced no reproductive toxicity to two generations of Sprague-Dawley rats even in the presence of parental toxicity at 3000 and 8000 ppm. Postnatal toxicity was observed in the offspring of both generations, but only in the presence of maternal toxicity. The no-observed-effect level (NOEL) for both parental and postnatal toxicity is 400 ppm, and the NOEL for reproductive toxicity is at least 8000 ppm.

Symposium on estrogens in the environment, III.

Symposium on estrogens in the environment, III.

Two-generation reproduction toxicity study with isopropanol in rats.

A two-generation reproduction toxicity study was conducted in rats with isopropanol. Thirty rats of each sex per group (P1) were dosed once daily by oral gavage with 0, 100, 500 or 1000 mg isopropanol kg-1 for at least 10 weeks prior to mating. Parental animals were mated within groups for up to 3 weeks. Parental females were dosed during mating, gestation and lactation; parental males were dosed during mating through delivery of their last litter sired. The P2 adults were selected from the F1 litters and were dosed for 10-13 weeks before mating to produce a single litter. Findings in the parental animals included increased lactation body weight gain in the mid- and high-dose females, increased liver and kidney weights in the mid- and high-dose groups of both sexes and centrilobular hepatocyte hypertrophy in some P2 males. There was also accumulation of hyaline droplets and other microscopic findings in the kidneys from the mid- and high-dose P1 males and from all treated groups of the P2 males. Increased mortality was observed in the high-dose F1 offspring during the early postnatal period, although no other clinical signs of toxicity were observed in the offspring of either generation. In addition, offspring body weight was reduced during the early postnatal period in the high-dose F1 males and in the high-dose F2 pups of both sexes. Eighteen out of 70 F1 weanlings in the 1000 mg kg-1 group died or were euthanized prior to P2 selection. No treatment-related post-mortem findings were observed in the offspring from either generation.(ABSTRACT TRUNCATED AT 250 WORDS)

A two-generation reproductive and developmental toxicity study of sucrose polyester

Sucrose polyester (SPE) is a mixture of hexa-, hepta- and octa-esters of fatty acids with sucrose, and has physical and organoleptic properties similar to those of conventional dietary fats. Because SPE is neither absorbed nor metabolized it forms a bulk lipid phase in the small intestine, resulting in effects on the absorption and enterohepatic circulation of lipid-soluble materials, such as cholesterol and fat-soluble vitamins. Such effects could potentially alter the physiology of animals to the extent of interfering with reproduction and/or the normal development of the embryo/foetus. To determine the likelihood of such phenomena, Sprague-Dawley rats were continuously fed SPE at dietary levels of 1, 5 or 10% along with controlled levels of vitamins A and E for two generations, with a reproductive and a teratogenic phase in each generation. Body-weight gain of rats fed SPE was comparable to that of the controls throughout the study, but feed consumption increased with increasing levels of SPE. Pregnancy or lactation had no effect on these growth patterns. Throughout the study, SPE had no deleterious effect on mating, conception, embryonic development, foetal or post-natal viability, or on post-natal growth. Nor was there any treatment-related histopathology. Thus, it is concluded that SPE would not represent a reproductive or teratogenic hazard to human consumers of products containing SPE.