Three-generation Reproduction Study Research Articles

Safety evaluation of curdlan as a food additive.

The EFSA Panel on Food Additives and Flavourings (FAF) provides a scientific opinion on the safety of curdlan as a new food additive used as firming and gelling agent, stabiliser, thickener. Curdlan is a high molecular weight polysaccharide consisting of β-1,3-linked glucose units, produced by fermentation from Rhizobium radiobacter biovar 1 strain NTK-u. The toxicological dataset consisted of sub-chronic, chronic and carcinogenicity, reproductive and developmental toxicity studies as well as genotoxicity. Invivo data showed that curdlan is not absorbed as such but is extensively metabolised by the gut microbiota into CO2 and other innocuous compounds. Curdlan was not genotoxic and was well-tolerated with no overt organ-specific toxicity. Effects observed at very high doses of curdlan, such as decreased growth and increased cecum weight, are common for indigestible bulking compounds and therefore considered physiological responses. In a combined three-generation reproductive and developmental toxicity study, decreased pup weight was observed during lactation at 7500 mg curdlan/kg body weight (bw) per day, the highest dose tested. The Panel considered the observed effects as treatment-related and adverse, although likely secondary to nutritional imbalance and identified a conservative no observed adverse effect level (NOAEL) of 2500 mg/kg bw per day. Despite the limitations noted in the dataset, the Panel was able to conclude applying the margin of exposure (MOE) approach. Given that curdlan and its break-down products are not absorbed and that the identified adverse effect is neither systemic nor local, no adjustment factor was deemed necessary. Thus, an MOE of at least 1 was considered sufficient. The highest exposure estimate was 1441 mg/kg bw per day in toddlers at the 95th percentile of the proposed maximum use level exposure assessment scenario. The Panel concluded that there is no safety concern for the use of curdlan as a food additive at the proposed uses and use levels.

Report on the two‐phase public consultation on the draft EFSA scientific opinion on bisphenol A (BPA)

Report on the two‐phase public consultation on the draft EFSA scientific opinion on bisphenol A (BPA)

Final Report of the Cosmetic Ingredient Review Expert Panel on the Safety Assessment of Polyisobutene and Hydrogenated Polyisobutene as Used in Cosmetics

Polyisobutene and Hydrogenated Polyisobutene are homopolymers of isobutene. These ingredients are produced in a wide range of molecular weights. Polybutene is a chemically related cosmetic ingredient previously determined to be safe as used in cosmetic products. Polyisobutene is used in cosmetic products as a binder, film former, and nonaqueous viscosity-increasing agent. Hydrogenated Polyisobutene functions as a skin-conditioning agent—emollient and nonaqueous viscosity-increasing agent with a wide range of uses in cosmetic formulations. The estimated octanol water partition coefficient for Hydrogenated Polyisobutene and Polybutene is log Kow of 13.27 and the estimated water solubility was 5.6 × 10–3 ng/L for Hydrogenated Polyisobutene and Polybutene. Acute oral toxicity testing demonstrated no effects other than lethargy in one rat study. The oral LD50 was >5.0 g/kg in rats. No short-term or subchronic animal toxicity data were available. A 2-year chronic oral toxicity study of Polybutene revealed no gross or microscopic pathological changes, and no changes in body weights or food consumption, hematological results, urology, or tumor formation that could be correlated with Polybutene ingestion, except that in the 20,000 ppm group, three out of six males that died between weeks 17 and 24 exhibited hematuria. In a 2-year chronic oral toxicity study of Polybutene in Beagle dogs, no abnormalities in body weight, food consumption, survival, behavioral patterns, hematology, blood chemistry, urinalysis, liver function, gross and histopathologic examinations, or organ weights and ratios were reported. In a three-generation reproductive study in Charles River albino rats that ingested Polybutene, none of the animals in successive generations differed from controls with regard to weight gain, litter size, the number of stillborn, and the number of viable pups during lactation. The survival, body weights, and reactions of test animals were comparable to those of controls. Neither Polyisobutene nor Hydrogenated Polyisobutene were ocular irritants, nor were they dermal irritants or sensitizers. Polyisobutene was not comedogenic in a rabbit ear study. Polyisobutene did not induce transformation in the Syrian hamster embryo (SHE) cell transformation assay, but did enhance 3-methylcholanthrene–induced transformation of C3H/10T1/2 cells. In a carcinogenicity study in mice, Polyisobutene was not carcinogenic, nor did it promote the carcinogenicity of 7,12-dimethylbenz(α)anthracene. Clinical patch tests uncovered no evidence of dermal irritation and repeat-insult patch tests with a product containing 4% Hydrogenated Polyisobutene or 1.44% Hydrogenated Polyisobutene found no reactions greater than slight erythema. These products also were not phototoxic or photoallergenic. The product containing 4% Hydrogenated Polyisobutene was not an ocular irritant in a clinical test. The Cosmetic Ingredient Review (CIR) Expert Panel recognized that there are data gaps regarding use and concentration of these ingredients. However, the overall information available on the types of products in which these ingredients are used and at what concentrations indicate a pattern of use, which was considered by the Expert Panel in assessing safety. Although there is an absence of dermal absorption data for Polyisobutene and Hydrogenated Polyisobutene, the available octanol water partition coefficient data and the low solubility in water suggest very slow absorption, so additional data are not needed. Gastrointestinal absorption is also not a major concern due to the low solubility of these chemicals. Although one in vitro study did report that Polyisobutene did promote cellular transformation, a mouse study did not find evidence of tumor promotion. Because lifetime exposure studies using rats and dogs exposed to Polybutene failed to demonstrate any carcinogenic or tumor promotion effect, and a three-generation reproductive/developmental toxicity study produced no adverse effects, the CIR Expert Panel does not believe these large, mostly insoluble polymers present any risks in the practices of use and concentration as described in this safety assessment.

Final Report of the Cosmetic Ingredient Review Expert Panel on the Safety Assessment of Polyisobutene and Hydrogenated Polyisobutene as Used in Cosmetics

Polyisobutene and Hydrogenated Polyisobutene are homopolymers of isobutene. These ingredients are produced in a wide range of molecular weights. Polybutene is a chemically related cosmetic ingredient previously determined to be safe as used in cosmetic products. Polyisobutene is used in cosmetic products as a binder, film former, and nonaqueous viscosity-increasing agent. Hydrogenated Polyisobutene functions as a skin-conditioning agent-emollient and nonaqueous viscosity-increasing agent with a wide range of uses in cosmetic formulations. The estimated octanol water partition coefficient for Hydrogenated Polyisobutene and Polybutene is log K(ow) of 13.27 and the estimated water solubility was 5.6 x 10(-3) ng/L for Hydrogenated Polyisobutene and Polybutene. Acute oral toxicity testing demonstrated no effects other than lethargy in one rat study. The oral LD(50) was > 5.0 g/kg in rats. No short-term or subchronic animal toxicity data were available. A 2-year chronic oral toxicity study of Polybutene revealed no gross or microscopic pathological changes, and no changes in body weights or food consumption, hematological results, urology, or tumor formation that could be correlated with Polybutene ingestion, except that in the 20,000 ppm group, three out of six males that died between weeks 17 and 24 exhibited hematuria. In a 2-year chronic oral toxicity study of Polybutene in Beagle dogs, no abnormalities in body weight, food consumption, survival, behavioral patterns, hematology, blood chemistry, urinalysis, liver function, gross and histopathologic examinations, or organ weights and ratios were reported. In a three-generation reproductive study in Charles River albino rats that ingested Polybutene, none of the animals in successive generations differed from controls with regard to weight gain, litter size, the number of stillborn, and the number of viable pups during lactation. The survival, body weights, and reactions of test animals were comparable to those of controls. Neither Polyisobutene nor Hydrogenated Polyisobutene were ocular irritants, nor were they dermal irritants or sensitizers. Polyisobutene was not comedogenic in a rabbit ear study. Polyisobutene did not induce transformation in the Syrian hamster embryo (SHE) cell transformation assay, but did enhance 3-methylcholanthrene-induced transformation of C3H/10T1/2 cells. In a carcinogenicity study in mice, Polyisobutene was not carcinogenic, nor did it promote the carcinogenicity of 7,12-dimethylbenz(alpha)anthracene. Clinical patch tests uncovered no evidence of dermal irritation and repeat-insult patch tests with a product containing 4% Hydrogenated Polyisobutene or 1.44% Hydrogenated Polyisobutene found no reactions greater than slight erythema. These products also were not phototoxic or photoallergenic. The product containing 4% Hydrogenated Polyisobutene was not an ocular irritant in a clinical test. The Cosmetic Ingredient Review (CIR) Expert Panel recognized that there are data gaps regarding use and concentration of these ingredients. However, the overall information available on the types of products in which these ingredients are used and at what concentrations indicate a pattern of use, which was considered by the Expert Panel in assessing safety. Although there is an absence of dermal absorption data for Polyisobutene and Hydrogenated Polyisobutene, the available octanol water partition coefficient data and the low solubility in water suggest very slow absorption, so additional data are not needed. Gastrointestinal absorption is also not a major concern due to the low solubility of these chemicals. Although one in vitro study did report that Polyisobutene did promote cellular transformation, a mouse study did not find evidence of tumor promotion. Because lifetime exposure studies using rats and dogs exposed to Polybutene failed to demonstrate any carcinogenic or tumor promotion effect, and a three-generation reproductive/developmental toxicity study produced no adverse effects, the CIR Expert Panel does not believe these large, mostly insoluble polymers present any risks in the practices of use and concentration as described in this safety assessment.

Sex ratio of the offspring of Sprague–Dawley rats exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in utero and lactationally in a three-generation study

Reports of a decreased male/female sex ratio in children born to males exposed to TCDD in Seveso, Italy, at a young age have sparked examinations of this endpoint in other populations exposed to TCDD or related compounds. Overall, the male/female sex ratio results reported in these studies, with slightly different age-exposed male populations, have shown mixed results. Experimental studies of the effects of in utero exposure to TCDD in laboratory animals have reported no effect on the f(1) sex ratio and mixed results for the sex ratio of the f(2) generation. In order to better understand the potential effects of TCDD on second generation sex ratio, we retrieved archived data from a comprehensive three-generation feeding study of TCDD in rats that was conducted and published in the 1970s, but which did not publish data on sex ratio of the offspring [Murray, F.J., Smith, F.A., Nitschke, K.D., Humiston, C.G., Kociba, R.J., Schwetz, B.A., 1979. Three-generation reproduction study of rats given 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in the diet. Toxicol. Appl. Pharmacol. 50, 241-252]. A re-examination of the original Murray et al. data found no statistically significant treatment-related changes in postnatal day 1 sex ratio in any generation of treated animals, consistent with one other relatively large study reporting on this endpoint. We discuss mechanistic data underlying a potential effect of TCDD on this endpoint. We conclude that the inconsistency in findings on sex ratio of the offspring of male rats exposed to TCDD in utero is likely due to random variation associated with a relatively small sample size, although differences between studies in strain of rat, dose regimen, and day of ascertainment of sex ratio cannot be ruled out.

Amended Final Report on the Safety Assessment of Polyacrylamide and Acrylamide Residues in Cosmetics1

Polyacrylamide is a polymer of controllable molecular weight formed by the polymerization of acrylamide monomers available in one of three forms: solid (powder or micro beads), aqueous solution, or inverse emulsions (in water droplets coated with surfactant and suspended in mineral oil). Residual acrylamide monomer is likely an impurity in most Polyacrylamide preparations, ranging from <1 ppm to 600 ppm. Higher levels of acrylamide monomers are present in the solid form compared to the other two forms. Polyacrylamide is reportedly used in 110 cosmetic formulations, at concentrations ranging from 0.05% to 2.8%. Residual levels of acrylamide in Polyacrylamide can range from <.01% to 0.1%, although representative levels were reported at 0.02% to 0.03%. Because of the large sizes of Polyacrylamide polymers, they do not penetrate the skin. Polyacrylamide itself is not significantly toxic. For example, an acute oral toxicity study of Polyacrylamide in rats reported that a single maximum oral dose of 4.0 g/kg body weight was tolerated. In subchronic oral toxicity studies, rats and dogs treated with Polyacrylamide at doses up to 464 mg/kg body weight showed no signs of toxicity. Several 2-year chronic oral toxicity studies in rats and dogs fed diets containing up to 5% Polyacrylamide had no significant adverse effects. Polyacrylamide was not an ocular irritant in animal tests. No compound-related lesions were noted in a three-generation reproductive study in which rats were fed 500 or 2000 ppm Polyacrylamide in their diet. Polyacrylamide was not carcinogenic in several chronic animal studies. Human cutaneous tolerance tests performed to evaluate the irritation of 5% (w/w) Polyacrylamide indicated that the compound was well tolerated. Acrylamide monomer residues do penetrate the skin. Acrylamide tested in a two-generation reproductive study at concentrations up to 5 mg/kg day(- 1) in drinking water, was associated with prenatal lethality at the highest dose, with evidence of parental toxicity. The no adverse effects level was close to the 0.5 mg/kg day(- 1) dose. Acrylamide tested in a National Toxicology Program (NTP) reproductive and neurotoxicity study at 3, 10, and 30 ppm produced no developmental or female reproductive toxicity. However, impaired fertility in males was observed, as well as minimal neurotoxic effects. Acrylamide neurotoxicity occurs in both the central and peripheral nervous systems, likely through microtubule disruption, which has been suggested as a possible mechanism for genotoxic effects of acrylamide in mammalian systems. Acrylamide was genotoxic in mammalian in vitro and in vivo assays. Acrylamide was a tumor initiator, but not an initiator/promoter, in two different mouse strains at a total dose of 300 mg/kg (6 doses over 2 weeks) resulting in increased lung adenomas and carcinomas without promotion. Acrylamide was tested in two chronic bioassays using rats. In one study, increased incidence of mammary gland tumors, glial cell tumors, thyroid gland follicular tumors, oral tissue tumors, uterine tumors and clitoral gland tumors were noted in female rats. In male rats, the number of tumors in the central nervous system (CNS), thyroid gland, and scrotum were increased with acrylamide exposure. In the second study, using higher doses and a larger number of female rats, glial cell tumors were not increased, nor was there an increase in mammary gland, oral tissue, clitoral gland, or uterine tumors. Tumors of the scrotum in male rats were confirmed, as were the thyroid gland follicular tumors in males and females. Taken together, there was a dose-dependent, but not statistically significant, increase in the number of astrocytomas. Different human lifetime cancer risk predictions have resulted, varying over three orders of magnitude from 2 x 10(- 3) to 1.9 x 10(- 6). In the European Union, acrylamide has been limited to 0.1 ppm for leave-on cosmetic products and 0.5 ppm for other cosmetic products. An Australian risk assessment suggested negligible health risks from acrylamide in cosmetics. The Cosmetic Ingredient Review (CIR) Expert Panel acknowledged that acrylamide is a demonstrated neurotoxin in humans and a carcinogen in animal tests, but that neurotoxic levels could not be attained by use of cosmetics. Although there are mechanisms of action of acrylamide that have been proposed for tumor types seen in rat studies that suggest they may be unique to the rat, the Panel was not convinced that these results could be disregarded as a species-specific finding with no relevance to human health and safety. Based on the genotoxicity and carcinogenicity data, the Panel does not believe that acrylamide is a genotoxic carcinogen in the usual manner and that several of the risk assessment approaches have overestimated the human cancer risk. The Panel did conclude, however, that it was appropriate to limit acrylamide levels to 5 ppm in cosmetic formulations.

Three-generation reproduction study of rats receiving acrylonitrile in drinking water

Acrylonitrile, a high volume organic chemical, was tested for reproductive effects in a three generation drinking water study with two matings per generation. Sprague–Dawley rats were exposed to acrylonitrile in drinking water at 0, 100, or 500 ppm. This corresponds to 0, 11±5 and 37±10 mg/kg, respectively, for males and 0, 20±3 and 40±8 mg/kg per day for the females, respectively. Water consumption was reduced in F0 rats in the 100 and 500 ppm groups. At 500 ppm, acrylonitrile reduced body weight gain and food intake of the first generation parental rats (F0). These parameters were not investigated at subsequent generations. The pup survival (both viability and lactation indices) was reduced at the 500 ppm treatment level in both matings of all three generations. Fostering the 500 ppm pups onto untreated mothers following the second mating lessened mortality, suggesting a maternal effect consistent with decreased water consumption. There was no remarkable change in the reproductive capacity in any of matings in rats at the 100 ppm concentration. In contrast, in all three generations, the body weights of the pups of the 500 ppm treatment level were reduced on Day 21 at both matings. No adverse findings were observed in the tissues of a limited number of third generation weanlings (F3b) upon gross and microscopic evaluation. No effect on the sciatic nerve was evident among the adult female rats held for 20 weeks after weaning of the second litter. There was a dose-related effect of acrylonitrile on gross masses in female rats at each parental generation held 20 weeks after the weaning of the second litter. Histopathological evaluation of these dams showed an increase in astrocytomas and zymbal gland tumors.

A limited three-generation reproduction study on hexachlorocyclohexane (HCH) in rats

Dietary feeding of technical hexachlorocyclohexane (HCH) at 125 and 250 ppm to rats have not shown any adverse effects on reproductive function and were comparable to control animals in a three-generation study. There were no major malformations, while some minor variants found were not compound or dose related. Despite some mild toxicological effects in rats of the P 0 generation, the litters of F 1B, F 2B and F 3B generations were devoid of any morphological or teratological changes. The presence of HCH residues in vital tissues of F 3B pups have indicated transmigration of HCH in preceding generations but not to an extent that produced adverse effects.

A Three-generation Reproduction Study on Polyglycerol Polyricinoleate (PGPR) in Wistar Rats

A series of toxicology studies were conducted in the 1950s and 1960s to investigate the toxicity of ADMUL WOL, a brand of polyglycerol polyricinoleate (PGPR). Included as part of these investigations was a three-generation reproduction study in rats. The control rats received a commercial pelletted stock diet and the treated rats were given the same diet ground with 1.5% (w/w) PGPR. A continuous breeding protocol was adopted, in which the breeding pairs were maintained until the female had produced five litters or when it became evident that breeding had ceased. The main focus of the study design was to observe any effect on breeding. The parameters measured in each of the three generations included number of litters per dam, average litter size, average weaning weights of males and females, litters per group showing 100% survival and total survival (%) at day 21. Growth was normal throughout the three generations and there were no deaths or clinical signs associated with the consumption of PGPR. The only significant change in breeding performance was a reduction in the percentage of animals weaned in the second generation, but as this occurred in the control group to a similar extent it was concluded that this was due to an unknown environmental factor and was not treatment related. A histological examination of selected tissues from those rats continued for 1 year failed to show any lesions which could be ascribed to the consumption of PGPR. In conclusion, rats fed 1.5% (w/w) PGPR showed no evidence of a cumulative effect on breeding performance over three generations.

Sucrose Acetate Isobutyrate (SAIB): Three-generation Reproduction Study in the Rat and Teratology Studies in the Rat and Rabbit

A three-generation reproduction study of sucrose acetate isobutyrate (SAIB) in Fischer 344 rats and teratology studies in Fischer 344 rats and New Zealand white rabbits were performed. Dietary SAIB concentrations to provide dose levels of 0, 0.5, 1.0 and 2.0g/kg body weight were used for the rat studies, and 0, 0.5, 0.85 and 1.2g/kg body weight doses of SAIB in corn oil were administered by gavage in the rabbit studies. F0 generation male rats were fed SAIB for 10wk, and female rats were fed SAIB for 2wk prior to mating. F1 generation rats were raised on the test diets to maturity, mated to produce F2a litters, and remated to produce the F2b litters that were examined for teratology. F2a rats were mated to study fertility indices for the F3 pregnancy. A decrease in female fertility compared with controls was noted at the highest dose of SAIB during breeding of the F1 generation to produce the F2a litters. No difference in fertility rate between controls and treated animals was noted in the results of the other three matings that were performed, and it was concluded that the reduction in female fertility was not related to SAIB treatment. No morphological abnormalities of soft tissue or skeleton were observed in the rat or rabbit teratology studies. The highest dose levels administered, 2.0gSAIB/kg body weight in the rat and 1.2gSAIB/kg body weight in the rabbit, were considered to be no-observed-adverse effect levels (NOAEL).

Exposure to TCDD during development permanently alters reproductive function in male Long Evans rats and hamsters: reduced ejaculated and epididymal sperm numbers and sex accessory gland weights in offspring with normal androgenic status.

Prenatal administration of relatively low doses of TCDD alters reproductive development and fertility of the progeny. Fertility was reduced in the progeny of Wistar rats exposed to 0.5 micrograms TCDD/kg/day from Gestational Day (GD) 6 to GD 15. In a three-generation reproduction study, TCDD reduced fertility of Sprague-Dawley rats in the F1 and F2 but not the F0 (no developmental exposure) generation at 0.01 microgram/kg/day in the diet. Furthermore, administration of TCDD on GD 15 (at 0.064 to 1 microgram/kg) both demasculinized and feminized morphology and behavior of Holtzman male rat offspring. Our objectives were to expand the observations of Mably et al. (1992, Toxicol, Appl. Pharmacol. 114, 97-107, 108-117, 118-126) on the effects of gestational administration of a single dose of TCDD to another strain of rat and another species, the hamster. In the first study, Long Evans (LE) hooded rats were dosed by gavage with 1 microgram TCDD/kg on GD 8 (during the period of major organogenesis) or GD 15 (the gestational day used by Mably et al.). In the second study, pregnant Syrian hamsters, a species relatively insensitive to the lethal effects of TCDD, were dosed on GD 11, equivalent to GD 15 in the rat, with TCDD at 2 micrograms/kg. When LE rats were dosed on GD 15, or when hamsters were dosed on GD 11, puberty (preputial separation) was delayed by about 3 days, ejaculated sperm counts were reduced by at least 58%, and epididymal sperm storage was reduced by 38%. Testicular sperm production was less affected. The sex accessory glands were also reduced in size in LE rat offspring treated on GD 15 despite the fact that serum testosterone (T), T production by the testis in vitro, and androgen receptor (AR) levels were not reduced. Some reproductive measures, such as anogenital distance and male sex behavior, were altered by TCDD treatment in rat but not hamster offspring. Since T and AR levels appeared normal in the sex accessory glands and the epididymis following perinatal TCDD exposure, the alterations in these tissues are not likely to have resulted from an alteration of the androgenic status of the male offspring.

Three-generation reproductive studies of a synthetic pyrethroid — cyhalothrin

The present study was carried out to understand the effect of cyhalothrin, a synthetic pyrethroid, on reproduction in mice. The study was designed as a three-generation reproduction study. Mice were given 2.5 and 5.0 ppm cyhalothrin/kg body weight orally. Daily cumulative body weight of the pregnant mice, number of pups, and cumulative body weight of pups were noted during the study. Compared with the control, body weight gain of cyhalothrin-treated parent mice of the first generation (for both concentrations) was less. As per Dunnet t-test, the weights of treated mice were comparable with control or were statistically nonsignificant. The other two generations did not show significant changes in body weight gain. Cyhalothrin fed orally did not affect the body weight gain of the pups in any of the generations. There was no significant difference in the viability index in any of the generations. Survival of the pups of dams given cyhalothrin was similar to that in the control.

Final Report on the Safety Assessment of Polyacrylamide

Polyacrylamide is a polymer of controllable molecular weight formed from the polymerization of acrylamide monomers. Average concentrations of the monomer were reported as less than 0.01% by several manufacturers. Polyacrylamide is used as a foam builder and stabilizer in shampoo products and as a vehicle in sunscreen preparations. An acute oral toxicity study of Polyacrylamide in rats reported that a single maximum oral dose of 4.0 g/kg body weight was tolerated. In a subchronic oral toxicity study in both rats and dogs, animals were given a maximum dose of 464 mg/kg body weight, with no signs of toxicity in any animals. Two separate studies in rats reported no absorption when the compound was administered by gavage. In a 2-year chronic oral toxicity study, rats fed between 500 and 10,000 ppm in their diet had no significant adverse effects. Similar results were obtained in dogs. A 2-year feeding study in rats fed up to 5.0% Polyacrylamide reported no significant adverse effects. Cutaneous tolerance tests performed to evaluate the irritation of Polyacrylamide indicated that the compound was relatively well tolerated. Undiluted Polyacrylamide applied to the conjunctival sac of the rabbit caused a very slight response. No compound-related lesions were noted in a three-generation reproductive study in which rats were fed either 500 or 2000 ppm Polyacrylamide. On the basis of data presented in this report, it is concluded that Polyacrylamide, with less than 0.01% acrylamide monomer content, is safe as a cosmetic ingredient as currently used.

Three-generation reproduction study with dioctyl sodium sulfosuccinate in rats

Groups of 30 male and 30 female rats (F0) were fed diets containing 0, 0.1, 0.5, or 1.0% dioctyl sodium sulfosuccinate (DSS) for 10 and 2 weeks, respectively. The F0 animals were then mated to produce an F1 litter. Groups of 30 male and 30 female F1 animals were fed the same dose levels for at least 10 weeks postweaning, and the breeding program was repeated to produce F2 animals. F3 animals were produced from F2 animals by the same procedure. The study was terminated with the F3 weanlings. Test diets were fed continuously throughout the study. All F0, F1, and F2 adults and F3 weanlings (one/sex/litter) were necropsied and given a macroscopic examination. There were no effects on reproductive function for parental animals of either sex during any of the three generations in this study. At the highest dose level (1.0% DSS), body weights were lower than those of controls during the premating phase for males in all three generations and for F1 and F2 females. Body weights for F1 and F2 males and females in the 0.5% dose group were also low during the premating phase. Pup weights on Lactation Day 0 were significantly lower than those of controls only for the high-dose group during the third generation. However, lower pup weight gains in the mid- and high-dose groups resulted in significantly lower pup weights on Day 21 for all three generations. Perinatal pup survival across three generations ranged from 96 to 100% for the control and treated groups. Pup survival ranged from 95 to 100% for controls, from 98 to 100% for low- and mid-dose groups, and from 91 to 99% for the high-dose group. There were no treatment-related mortality and antemortem or macroscopic observations. In summary, DSS administered in the diet to three successive generations of rats at levels of 0.5 and 1.0% caused a reductions in body weights for parental males in all generations and for F1 and F2 females. Pup weights at the 0.5 and 1.0% dose levels were also lower than those of the control in all three generations. However, the reduced body weights did not interfere with development of normal reproductive performance. DSS at levels up to 1.0% had no effects on the reproductive function of either sex in any generation and produced no treatment-related antemortem or macroscopic observations.

Multigeneration study of FD & C Red No. 3 (erythrosine) in Sprague-Dawley rats

Sprague-Dawley rats received dietary admixtures containing 0.0, 0.25, 1.0 or 4.0% FD & C Red No. 3 (25 rats/sex/group) in a three-generation reproduction study. Each generation was bred twice and breeders for subsequent generations were selected after weaning of the second mating from each generation. There were no compound-related adverse effects on reproductive indices and no gross anomalies were observed. The body weights of parents and pups were significantly reduced ( P < 0.05) in all generations at the 4.0% dietary concentration. Maternal body-weight gain during gestation was frequently reduced in the 1.0 and 4.0% groups. The conservative no-observed-adverse-effect level established in this study was 0.25% (approximately 149 and 255 mg/kg body weight/day for males and females, respectively).

Three-Generation Reproduction Study with Dioctyl Sodium Sulfosuccinate in Rats

Three-Generation Reproduction Study with Dioctyl Sodium Sulfosuccinate in Rats

Three-generation reproductive study of cocoa powder in rats

Male and female Sprague-Dawley rats were continuously exposed to dietary cocoa powder at levels of 0.0, 1.5, 3.5 or 5.0% for three generations. During the initial 12-wk growth periods for the F 0-, F 1b- and F 2b-generation rats, mean methylxanthine exposures (mg/kg/day) for males/females were 30 36 , 72 86 and 104 126 for the 1.5, 3.5 and 5.0% cocoa powder groups, respectively. No consistent dose-related effects on any of the monitored reproductive indices (mating, fertility, conception, gestation, viability or lactation) were noted over three generations. Minor reductions in mean body weight relative to controls at wk 12 were observed in male rats exposed to 3.5 or 5.0% cocoa powder and female rats exposed to 5.0% cocoa powder in the F 1b and F 2b generations. Renal tubular mineralization in the F 0-generation male rats in the 5.0% cocoa powder group was the only statistically elevated histomorphological lesion observed. Plasma cholesterol concentrations in F 1b-generation rats were elevated, but cocoa powder did not affect this parameter consistently across multiple generations. Thus, continuous cocoa powder consumption by rats at levels as high as 5.0% of the diet was without effect on reproductive capacity under the conditions of a standard three-generation evaluation.

Three‐generation reproduction study with caprolactam in rats

In a three-generation reproduction study, rats were given caprolactam in the diet of 0, 1000, 5000 and 10,000 ppm. No treatment-related effects were observed in the parental animals with respect to mortality, clinical signs, reproductive performance or gross pathology findings. Consistently lower body weights were noted in the P2 and P3 mid- and high-dose males and females. Consistently lower mean food consumption values were noted in the P2 and P3 mid- and high-dose males and the high-dose females. These differences were generally significant (P less than or equal to 0.05) in the high-dose group of both sexes. Compound-related histopathologic findings noted in the high-dose P1 males consisted of a slight increase in the severity of spontaneous nephropathies, occasionally accompanied by granular casts. The offspring data revealed no treatment-related effect with respect to gross appearance, gross pathology, survival, number of pups, percentage of male pups or kidney weight. Analysis of the offspring body weights on Days 1, 7 and 21 of lactation revealed consistently and generally significant lower mean values in the high-dose male and female animals of all filial generations. The mean body weights of both sexes in the mid-dose group were generally lower than those of the controls. The effects on mean body weight, mean food consumption and the group increases in the severity of nephropathy, accompanied by the presence of granular casts in some animals, are considered to be related to the administration of caprolactam.

Three-generation reproduction study on carmine of cochineal in the rat

Carmine was fed continuously to male and female rats over three generations at dietary concentrations that provided intakes of 50, 150 or 500 mg carmine/kg body weight/day. In adult animals of all generations there were no effects of treatment on body-weight gain, food and water intakes or fertility. At autopsy the weights and the gross and microscopic appearance of the organs were normal. In the teratological investigations, examination of the foetal skeletons of the F 3 generation revealed a slightly more advanced stage of ossification in all treated groups compared to those of the control. Survival, growth and development of offspring were similar in each group apart from a slight delay in the time of tooth eruption in the 150- and 500-mg/kg groups of the first and second generations. This was not seen in the final generation. It is concluded that carmine had no untoward effects on the growth and fertility of adult rats, or on the ante- and postnatal development of their offspring when given continuously at doses of up to 500 mg/kg body weight/day in the diet throughout all phases of mating, gestation, lactation, weaning and adult life over three successive generations.

A three-generation reproduction study of Ponceau 4R in the rat

Ponceau 4R was fed to three generations of rats, at dietary concentrations to provide 0, 50, 500 or 1250 mg/kg body weight/day. In each generation treated groups consisted of 36 rats of each sex while 60 females served as controls. Apart from the F 0 generation, which started treatment as weanlings, treatment was continued throughout the study, providing in utero exposure of all offspring. The F 0 generation was bred twice, on the first occasion to provide animals for the next generation and for a long-term study, and a second time to provide data on in utero and post-partum development. In each generation approximately one third of the females from each group were killed before parturition to provide data on in utero development. The foetuses from these animals were examined for skeletal abnormalities. Remaining animals were allowed to litter and the offspring were monitored for 21 days after birth for survival and development. All animals were killed and subjected to a post-mortem examination which, for a proportion of each group in each generation, included recording of organ weights. Although a few adult rats died during the study these deaths were not associated with treatment. Fur of the treated animals was coloured pink, and faeces and caecal contents of animals from the two highest dose groups were yellow, the faeces also being softer than those of the controls. Treatment had no observed effect on clinical observations, body weight or food and water intake at any stage of the study. Animals fed the two highest doses for prolonged periods had enlarged caeca, but this effect was not seen in weanling animals on the same treatment. Neither the caecal enlargement nor the liver weights seen in the F 2 and F 3 offspring were considered to be an adverse effect of treatment. No treatment-related effects were seen in the uterine contents of females at any generation, but the skeletons of treated foetuses showed a slightly more advanced development than those of the controls. Postnatal development of offspring was not affected by treatment at any stage of the study. Tissues from the F 3 animals were examined by light microscopy and revealed no treatment-related effects. It is concluded that the no-adverse-effect level for Ponceau 4R is 1250 mg/kg body weight/day.