Subchronic toxicity of a fluoroalkylethanol mixture in rats

The objective of this study was to evaluate the subchronic toxicity of a commercial fluoroalkylethanol mixture, which is an intermediate in the production of fluoroorganic compounds that are used as protectants and surfactants. The test substance was administered daily by gavage to Sprague-Dawley rats as a suspension in aqueous methylcellulose. The dosages were 0, 25, 100, or 250 mg kg(-1) day(-1). A 1- and 3-month recovery period was included to evaluate the reversibility of toxic effects. No test substance-related mortality or neurotoxicity occurred. Body weights and/or nutritional parameters were significantly reduced at 100 and 250 mg kg(-1) day(-1), and these effects were reversible. Broken and absent teeth were observed in rats dosed with 250 mg kg(-1) day(-1), and microscopic tooth lesions (ameloblast degeneration/disorganization) occurred at 100 and 250 mg kg(-1) day(-1) and persisted with decreased severity throughout recovery. Decreased red cell mass parameters occurred at 90 days in the 250 mg kg(-1) day(-1) group, but red cell counts were normal thereafter during recovery. A persistent elevation of liver weights was seen in groups given > or =100 mg kg(-l) day(-1). The increased weights correlated with microscopic hepatocellular hypertrophy only in males and females administered 250 mg kg(-1) day(-1). Hepatic beta-oxidation was increased in a dose-dependent manner and persisted through 1 month of recovery at 250 mg kg(-1) day(-1). Increased kidney weights were observed at 25 (females only), 100, and 250 mg kg(-1) day(-1). These elevated weights persisted in the high dose after recovery and correlated with microscopic tubular hypertrophy (males only). Thyroid follicular hypertrophy was present at 100 and 250 mg kg(-1) day(-1) but was not present after recovery. Total fluorine in whole blood increased with continuous dosing and achieved steady state in approximately 42 days. Both plasma and urine fluoride levels were elevated in a dose-dependent manner. Under the conditions of the study, the no-observed adverse effect level for this mixture was 25 mg kg(-1) day(-1) for subchronic toxicity.     

Evaluation of the reproductive and developmental toxicity of the D-003, a mixture of long-chain fatty acids, in rats and rabbits

D-003 is a mixture of long-chain fatty acids isolated and purified from sugar cane wax with cholesterol-lowering properties. D-003 given orally (500 and 1000 mg/kg/day) to female rats for 15 days prior to mating, through mating and gestation to day 21 of lactation and male rats for 4 weeks prior and during mating did not induce toxic effects on reproduction. There were no significant reductions in the number of animals that conceived, in the numbers of pups born to those that did conceive, in the numbers of pups that survived until weaning, and in their body weights at weaning. Drug-treated and control groups’ offspring were comparable in growth, physical and behavioral development, spontaneous activity and reproductive performance.

Pregnant New Zealand rabbits were given D-003 as oral doses of 500 and 1000 mg/kg/day on days 6 through 18 of gestation without any evidence of embryotoxicity or teratogenicity. The no-observed-effect dose in these two experimental studies was 1000 mg/kg/day. After assessment of the potential of high doses of D-003 to act on developing embryo and reproduction process, no evidence supports the conclusion that D-003 is a reproductive and developmental toxicant/teratogen.     

Evaluation of the reproductive and developmental toxicity of aluminium ammonium sulfate in a two-generation study in rats

Aluminium ammonium sulfate (AAS) was tested for reproductive/developmental toxicity in a two-generation study. Male and female rats were continuously given AAS in drinking water at 0, 50, 500 or 5000 ppm. Water consumption was decreased in all AAS-treated groups, and the body weight of parental animals transiently decreased in the 5000 ppm group. In either generation, no compound-related changes were found in estrous cyclicity, sperm parameters, copulation, fertility and gestation index, number of implantations and live birth pups, sex ratios of pups or viability during the preweaning period. Male and female F1 pups in the 5000 ppm group showed a lower body weight on postnatal day 21, while there were no differences in the birth weight of F1 and F2 pups between the control and AAS-treated groups. Preweaning body weight gain in F2 males and females indicated a similar decreasing tendency at 5000 ppm. In F1 and F2 weanlings, the weight of the liver, spleen and thymus decreased at 5000 ppm, but no histopathological changes were found in these organs. In F1 females in the 5000 ppm group, vaginal opening was delayed slightly. There were no compound-related changes in male preputial separation or in other developmental landmarks. In behavioral tests conducted for F1 animals at 4-6 weeks of age, no compound-related changes were found in spontaneous locomotor activity and performance in a water-filled multiple T-maze. In conclusion, the NOAEL of AAS for two-generation reproductive/developmental toxicity was considered to be 500 ppm in rats. Considering the aluminium content in the basal diet, the total ingested dose of aluminium from drinking water and food in this 500 ppm group was calculated to be 5.35 mg Al/kg bw/day.     

Evaluation of potential reproductive and developmental toxicity of potassium perfluorohexanesulfonate in Sprague Dawley rats

This study evaluates the potential reproductive and developmental toxicity of perfluorohexanesulfonate (PFHxS), a surfactant found in sera of the general population. In a modified OECD 422 guideline-based design, 15 rats per sex and treatment group (control, 0.3, 1, 3, and 10 mg/kg-d) were dosed by gavage with potassium PFHxS (K⁺PFHxS) or vehicle (0.5% carboxymethylcellulose) 14 days prior to cohabitation, during cohabitation, and until the day before sacrifice (21 days of lactation or presumed gestation day 25 (if not pregnant) for females and minimum of 42 days of treatment for males). Offspring were not dosed by gavage but were exposed by placental transfer in utero and potentially exposed via milk. Evaluations were made for reproductive success, clinical signs, body weight, food consumption, estrous cycling, neurobehavioral effects, gross and microscopic anatomy of selected organs, sperm, hematology, clinical pathology, and concentration of PFHxS in serum and liver. Additional three rats per sex per group were added to obtain sera and liver samples for PFHxS concentration determinations during the study. No reproductive or developmental effects were observed. There were no treatment-related effects in dams or offspring. K⁺PFHxS-induced effects noted in parental males included: (1) at all doses, reductions in serum total cholesterol; (2) at 0.3, 3, and 10 mg/kg-d, decreased prothrombin time; (3) at 3 and 10 mg/kg-d, increased liver-to-body weight and liver-to-brain weight ratios, centrilobular hepatocellular hypertrophy, hyperplasia of thyroid follicular cells, and decreased hematocrit; (4) at 10 mg/kg-d, decreased triglycerides and increased albumin, BUN, ALP, Ca²⁺, and A/G ratio. Serum and liver concentrations of PFHxS are reported for parents, fetuses, and pups. PFHxS was not a reproductive or developmental toxicant under study conditions.     

The rabbit as a model for reproductive and developmental toxicity studies

The rabbit has many advantages as a nonrodent and second model for assessing the effects of toxic agents on semen quality, fertility, developmental toxicity, and teratology. The male and female reproductive systems of the rabbit are described, and data on growth, sexual development and reproduction are compared with mice, rats, and humans. Techniques for semen collection and evaluation in the male, and artificial insemination, superovulation, embryo culture, and embryo transfer in the female are included as useful procedures in toxicity testing. Examples of the use of rabbits and experimental replication for toxicity testing are given. Special features of the visceral yolk sac and development of the chorioallantoic placenta of the rabbit are compared with rodents. The rabbit extraembryonic membranes more closely resemble the human than do the rodents, in some respects. The use of the rabbit in developmental toxicity and teratology studies is discussed.     

Weight-of-the-evidence review of acrylonitrile reproductive and developmental toxicity studies

Risk assessment of acrylonitrile (AN) toxicity to humans has focused on potential carcinogenicity and acute toxicity. Epidemiological studies from China reported reproductive and developmental effects in AN workers, including infertility, birth defects, and spontaneous abortions. A weight-of-the-evidence (WoE) evaluation of the AN database assessed study strength, characterized toxicity, and identified no-observed-adverse-effect levels (NOAELs). The epidemiological studies do not demonstrate causality and are not sufficiently robust to be used for risk assessment. Rodent developmental studies showed fetotoxicity and malformations at maternally toxic levels; there was no unique developmental susceptibility. NOAELs for oral and inhalation exposures were 10?mg/kg/day and 12?ppm (6?h/day), respectively. Drinking-water and inhalation reproductive toxicity studies showed no clear effects on reproductive performance or fertility. Maternally toxic concentrations caused decreased pup growth. The drinking-water reproductive NOAEL was 100?ppm (moderate confidence due to study limitations). The inhalation exposure reproductive and neonatal toxicity high confidence NOAEL was 45?ppm (first generation 90?ppm) (6?h/day). The inhalation reproductive toxicity study provides the most robust data for risk assessment. Based on the WoE evaluation, AN is not expected to be a developmental or reproductive toxicant in the absence of significant maternal toxicity.     

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.     

Subchronic, reproductive, and developmental toxicity of a fluorotelomer-based urethane polymeric product

A commercial fluorotelomer-based urethane polymeric dispersion, consisting of polymer, surfactant, and water, was evaluated in subchronic, reproduction, and developmental toxicity studies. The dispersion was administered daily by gavage to rats at dosages of 0, 50, 250, or 1000 mg polymer/kg/day or with 70 mg/kg/day of the sulfonate surfactant. Dose levels of 0, 50, 250, or 1000 mg polymer/kg/day were also used for the reproductive and developmental studies. Nasal olfactory epithelial degeneration and necrosis occurred in all dose groups in the 90-day study. Nasal adhesions were observed only in rats administered surfactant alone. Liver-enzyme alterations at 250 and 1000 mg/kg were considered to be potentially adverse effects. The subchronic no-observed-adverse-effects level (NOAEL) was 50 mg/kg. For the reproduction study, rats were dosed for 10 weeks prior to cohabitation and throughout mating, gestation, and lactation. There were no effects on reproductive function in males or females at any dosage. Thyroid weight was decreased in the 250 and 1000 mg/kg day F(1) groups unaccompanied by microscopic effects. In the developmental toxicity study, female rats were dosed from gestation days 6-20; there was no test-substance-related embryolethality, nor was there any dose-related increase in either fetal malformations. Fetal weight was minimally decreased at 1000 mg/kg/day in the presence of slight maternal toxicity; the NOAEL for developmental parameters was 250 mg/kg/day. The polymeric product was not a specific developmental or reproductive toxin.     

益母草碱对胚胎-胎仔发育毒性和遗传毒性的评价

目的 检测益母草碱的发育毒性和遗传毒性。方法 在SD孕鼠妊娠第6~15天经口灌胃给予500、1 000和2 000 mg/kg体重的益母草碱,同时设溶媒对照组,经口灌胃0.5% CMC-Na溶液。妊娠第20天剖杀孕鼠,分析其生殖毒性。分别采用反映基因突变的鼠伤寒沙门菌回复突变试验（Ames试验）、反映染色体畸变的细胞染色体畸变试验（体外培养CHO）和ICR小鼠骨髓微核试验（体内）检测益母草碱的遗传毒性。结果 在500、1 000和2 000 mg/kg剂量益母草碱的作用下孕鼠的增重与对照组相比,差异均无统计学意义;各受试剂量组孕鼠各项指标与对照组相比,差异均无统计学意义;各剂量组胎鼠各类指标与溶媒对照组相比,无明显差异。Ames试验结果提示：在0.5、5、50、500、5 000 μg/皿受试剂量下,在有或无代谢活化S9系统时,与溶媒对照组相比,受试物对组氨酸缺陷型鼠伤寒沙门菌（TA97、TA98、TA100、TA102及TA1535）所诱发的回复突变菌落数均相近。染色体畸变试验结果显示：250、500和1 000 μg/ml 3个剂量的受试物,对有或无代谢活化系统S9培养的CHO细胞的染色体畸变率无明显影响。微核试验显示100、500和2 000 mg/kg各个剂量组对ICR小鼠的微核诱发率与溶媒对照组比较均无显著差异（P>0.05）。结论 益母草碱在500、1 000和2 000 mg/kg剂量下未观察到明显的母体毒性、胚胎毒性、胎儿毒性和致畸作用。益母草碱对鼠伤寒沙门菌无致突变性,对哺乳动物培养细胞的染色体无致畸变作用,对ICR小鼠无诱发骨髓嗜多染红细胞微核的效应。上述结果表明在本试验条件下,益母草碱无发育和遗传毒性。     

Evaluation of the developmental toxicity of acetyl cedrene

The developmental toxicity of acetyl cedrene (AC), a widely used fragrance ingredient, was evaluated in pregnant Sprague-Dawley rats (25/group). Gavaged dosages of 0 (corn oil), 25, 50, or 100 mg/kg/day were administered on days 7 through 17 of gestation (GDs 7 to 17). First and last day dosing suspensions were analyzed for AC content. All rats were observed daily for viability, clinical signs, abortions, and premature deliveries. Body weights were recorded at frequent intervals. Cesarean-sectioning and necropsy examinations were performed on GD 21. Uteri were examined for number and distribution of implantations, live and dead fetuses, and early and late resorptions. The number of corpora lutea in each ovary was also recorded. Fetuses were weighed and examined for gender and gross external changes and soft tissue or skeletal alterations. Totals of 25, 23, 21, and 24 rats became pregnant in the 0 (control), 25, 50 and 100 mg/kg/day groups, respectively, and analysis of dosage preparations verified that administered dosages reflected calculated dosages +/-10%. No deaths or premature deliveries occurred in the study. Clinical signs included excessive salivation, which was attributed to the administration of AC. When compared to controls, significant reductions in feed consumption and body weight gains occurred only at 100 mg/kg/day. Both absolute (g/day) and relative (g/kg/day) feed consumption values were significantly decreased on GDs 7 to 12. Relative values were decreased significantly on GDs 15 to 18. Body weight gains were significantly reduced on GDs 7 to 10. Mean maternal body weights remained significantly lower than controls on GDs 9 to 14, but a marked compensatory increase in feed consumption on GDs 15 to 18 prevented further deterioration in body weight gains. No cesarean-sectioning or litter parameters were affected by dosages of AC and necropsy of the dams after cesarean section did not reveal any gross changes attributable to AC. No gross external, soft tissue, or skeletal fetal alterations (malformations or variations) were attributed by dosages AC. The average number of ossifications sites per fetus per litter did not differ among the groups. Based on these data, maternal and developmental no-observable-adverse-effect levels (NOAELs) of 50 and 100 mg/kg/day, respectively, were established for AC.     

Endocrine-disrupting activity in carbendazim-induced reproductive and developmental toxicity in rats

This study was designed to investigate the endocrine-disrupting activity of carbendazim-induced reproductive and developmental toxicity in Sprague-Dawley rats treated orally with the fungicide. Cotreatment of male rats with 675 mg/kg carbendazim and 50 or 100 mg/kg flutamide, an androgen receptor antagonist, once daily for 28 d blocked decrease of testis weight induced by treatment with carbendazim alone. The cotreatment prevented losses of spermatozoa and cell morphology and decrease of sperm concentration induced by carbendazim. Premating treatment of male and female rats with 200 mg/kg carbendazim for 28 d produced androgenic effects including incomplete development of uterine horn, enlargement of uretha, absence of vagina, and induction of seminal vesicles in female offspring, without marked effects in male offspring. Premating treatment with 100mg/kg benomyl, the parent compound of carbendazim, resulted in incomplete development of uterine horn and absence of vagina in female offspring and produced testis and epidydimis atropy in male offspring. Treatment of male rats with 25, 50, 100, 200, 400, and 800 mg/kg carbendazim for 56 d produced dose-dependent increases of androgen receptor concentrations in testis and epididymis. Additions of 5, 50, and 500 microM carbendazim to testis extract from untreated rats replaced binding of [3H]-5 alpha-dihydrotestosterone to androgen receptor in a concentration-dependent manner. The present study demonstrates that reproductive toxicity induced by carbendazim is blocked by an androgen receptor antagonist in male rats and developmental toxicity of the fungicide shows androgenic properties in female offspring. These results suggest that androgen- and androgen receptor-dependent mechanisms are possibly involved in carbendazim-induced toxicity.     

Assessment of the developmental and reproductive toxicity of diiodomethyl-p-tolylsulfone in rats and rabbits

Diiodomethyl-p-tolylsulfone (DIMPTS) was tested in developmental toxicity (DT) and reproductive toxicity studies. In the rat DT study, DIMPTS was administered at 0, 100, 300 or 1000 mg/kg/day. Maternal toxicity as evidenced by reductions in body weight gain or feed consumption at 1000 and, to a lesser extent, 300 mg/kg/day. The only developmental effect was umbilical hernia at 1000 mg/kg/day; therefore, NOELs for maternal and developmental toxicity were 100 and 300 mg/kg/day, respectively. In the rabbit DT study, NZW rabbits were gavaged with 0, 0.05, 0.5 and 2mg/kg/day DIMPTS. The NOEL for maternal toxicity was 0.5mg/kg/day, based on thyroid weight increase with histopathology. There were no observed developmental effects. In the two-generation study, CD rats were fed 0, 2.5, 10 or 40 mg/kg/day DIMPTS. Increased thyroid weight and histopathology were observed at all doses with associated pituitary findings in males. Reproductive toxicity at 40 mg/kg/day consisted of increased postimplantation loss, decreased gestation survival and two cases of dystocia, while litter size, pup survival/weight were affected at 10 and 40 mg/kg/day. The NOEL for parental toxicity could not be determined, while the NOEL for reproductive toxicity was 2.5mg/kg/day. The maternal thyroid and reproductive effects in this study were consistent with iodine toxicity.     

Critical aspects in reproductive and developmental toxicity testing of environmental chemicals

The process of toxicity testing of environmental chemicals is ruled by a framework of guidelines (OECD, OPPTS, etc.). The present paper will describe the process from the biological tests for environmental chemicals up to potential labelling and will focus on some critical aspects in this cascade of events. It is also the aim of this paper to give an overview of the existing documents and draft documents relevant for this field and available in the internet. Based on the current situation, the following points are discussed as critical issues: life stage considerations and their implications on testing, usefulness of investigations in juvenile animals, requirements for ADME studies, design and endpoints in fertility studies, use and usefulness of developmental milestones, performance of special studies versus one-study-design, considerations on transplacental carcinogenicity and early aging, significance of maternal/parental toxicity, application of triggers to justify studies, inclusion of new endpoints into test guidelines, and test strategies applied. Based on this, the usefulness of risk considerations in the current EU classification system for toxicity to reproduction as well as potency considerations will be discussed and suggestions will be made to improve the basic requirements for chemical testing which have remained relatively unchanged over the past 20 years.     

Current status and future progress of reproductive/developmental toxicity test

Currently, the European Centre for the Validation of Alternative Methods in the EU appears to be at the forefront of the development of alternative methods for developmental toxicity test (reproductive/developmental toxicity test). Why is it difficult to develop alternative methods for developmental toxicity test in comparison with other toxicity tests? In developmental toxicity test, chemical substances first enter the bloodstream and then reach the placenta via metabolism in the liver and other organs. After further metabolism in the placenta, chemical substances finally reach the fetus, where they affect fetal development. The difference in the in vivo route of chemical substances is an important reason for the difficulty in the establishment of new methods for developmental toxicologic test in comparison with general toxicity tests. According to the EU, the use of "in silico" techniques for developmental toxicity test may be difficult, and I agree with this. The in silico technique is basically a method for prediction of toxicologic effects from existing data, and cannot predict new effects, because data obtained by developmental toxicologic test are too complex. Three techniques are now being examined to overcome the difficulty in changing the method of developmental toxicologic test: the technique utilizing embryonic stem cells; micromass culture technique; and the whole embryonic culture technique. In this symposium, the current status of developmental toxicity tests and the three techniques being examined in the EU are introduced, and opinions on future progress are presented.