Extended One-Generation Reproductive Toxicity (EOGRT) study of benzoic acid in Sprague Dawley rats.

Benzoic acid (BA) was administered in the diet to male and female Sprague Dawley Crl:CD(SD) rats in an OECD Test Guideline 443 Extended One-Generation Reproductive Toxicity (EOGRT) study to test for effects that may occur as a result of pre- and postnatal exposure. The study included cohorts of F1 offspring to evaluate potential effects of benzoic acid on reproduction, the developing immune system, and the developing neurological system with the inclusion of learning and memory assessments. Benzoic acid was incorporated in the diet at concentrations of 0, 7,500, 11,500, and 15,000 mg/kg diet (ppm). These concentrations were selected based on the results of preliminary studies, and, based on average food consumption, were intended to supply BA doses of approximately 0, 500, 750, and 1000 mg/kg bw/day. To avoid exceeding these target dose levels, the dietary concentrations were adjusted (based on historical control body weight and food consumption data) to maintain the target mg/kg bw/day dose levels during those life periods when food intake per unit of body weight was increased to support milk production by females (gestation and lactation) and rapid pup growth (post-weaning). In the parental (F0) generation, survival, clinical observations, organ weights, pathology, hematology, serum chemistry, urinalysis, and bile acids were unaffected by BA administration. Reproductive parameters were also unaffected by BA administration. In the F1 generation, survival, growth and developmental landmarks, organ weights, pathology, immunotoxicity assessment, and neurotoxicity and neurobehavioral parameters such as auditory startle response, locomotor activity, learning and memory assessments were unaffected by BA administration, as were clinical pathology (hematology, serum chemistry, urinalysis, bile acids and thyroid hormones) and reproductive performance. Similarly, no adverse effects or systemic toxicity were observed in the F2 generation. Overall, the highest dietary concentration (15,000 ppm), providing a dosage of approximately 1000 mg/kg bw/day, was the NOAEL for benzoic acid in this EOGRT study.

Is there a rationale for direct dosing of chemicals to nursing pups in the EOGRTS (OECD 443)?

In OECD guideline 443 - Extended One Generation Reproductive Toxicity Study (EOGRTS) - to be used for testing industrial and agrochemicals, it has been indicated that careful consideration of benefits and disadvantages should be made prior to conducting direct-dosing studies in nursing pups. Nursing pups will not be directly dosed in dietary and drinking water studies whereas in oral gavage studies this possibility exists. Besides the risk of intubation trauma and overdosing due to direct exposure and exposure via the mother's milk, direct dosing could lead to a different hazard assessment of chemicals depending on the choice of the route of administration. In addition, in case of industrial and agrochemicals used in industrial or professional settings only, there will never be direct exposure of newborns. Moreover, direct dosing of nursing pups is an artificial, non-physiological, route of exposure and as such it would hamper risk assessment. It should therefore only be considered in exceptional cases and justified on a case-by-case approach.

Implementing the extended one-generation reproductive toxicity study (EOGRTS): important points to consider.

The hallmark of the extended one-generation reproductive toxicity study (EOGRTS) is that, based on certain criteria or triggers, selected offspring are assigned at weaning to different cohorts for further investigation of sexual maturation, reproductive organ integrity and function, neuropathological and behavioral endpoints, and/or immune function. The triggers allow for a more customizable design based directly on the data, while minimizing animal usage. Compared to the two-generation reproductive toxicity study, the EOGRTS design increases the number, extent, and duration of F1-offspring assessments resulting in more thorough and efficient utilization of the first generation while excluding the second generation of offspring unless triggered. Therefore, the EOGRTS has the potential to reduce the number of rats required by nearly 1200 animals per study. When performing the EOGRTS, the complexity of this study should not be underestimated and experienced flexible testing laboratories with sufficient resources and historical control data for all parameters are essential. The aim of this review is to discuss the important aspects of this challenging study design and to share our knowledge on the implementation of this study in our laboratories. In addition, we elaborate on the type of criteria for expansion of the study and logistical considerations. Altogether, this review can be used as guidance by other labs, study monitors, and registration officers.

Developmental immunotoxicity of chemicals in rodents and its possible regulatory impact.

Around 25% of the children in developed countries are affected with immune-based diseases. Juvenile onset diseases such as allergic, inflammatory and autoimmune diseases have shown increasing prevalences in the last decades. The role of chemical exposures in these phenomena is unclear. It is thought that the developmental immune system is more susceptible to toxicants than the mature situation. Developmental immunotoxicity (DIT) testing is nowadays not or minimally included in regulatory toxicology requirements. We reviewed whether developmental immune parameters in rodents would provide relatively sensitive endpoints of toxicity, whose inclusion in regulatory toxicity testing might improve hazard identification and risk assessment of chemicals. For each of the nine reviewed toxicants, the developing immune system was found to be at least as sensitive or more sensitive than the general (developmental) toxicity parameters. Functional immune (antigen-challenged) parameters appear more affected than structural (non-challenged) immune parameters. Especially, antibody responses to immune challenges with keyhole limpet hemocyanine or sheep red blood cells and delayed-type hypersensitivity responses appear to provide sensitive parameters of developmental immune toxicity. Comparison with current tolerable daily intakes (TDI) and their underlying overall no observed adverse effect levels showed that for some of the compounds reviewed, the TDI may need reconsideration based on developmental immune parameters. From these data, it can be concluded that the developing immune system is very sensitive to the disruption of toxicants independent of study design. Consideration of including functional DIT parameters in current hazard identification guidelines and wider application of relevant study protocols is warranted.

Time Course for Onset and Recovery from Effects of a Novel Male Reproductive Toxicant: Implications for Apical Preclinical Study Designs.

In the pharmaceutic ICH S5(R2) guidelines for reproductive toxicity testing, a premating dose duration of 14 days is considered sufficient for assessment of male fertility for compounds that are not testicular toxicants. A novel α7 subtype of nicotinic acetylcholine receptor (α7nAChR) agonist, originally intended for treatment of Alzheimer's disease, did not cause changes in sperm counts, motility, or testicular histopathology in rat toxicity studies of up to 6 months duration. However, profound decrements in male fertility (reduced pregnancy rates and litter sizes) occurred after 11 weeks of dosing in male rats. In two time-course investigations, dosed male rats were paired with undosed females after 5, 14, and 28 daily doses and again after 2 and 4 weeks off-dose. Effects on male fertility were undetectable after 5 days. After 14 days, there was no effect on pregnancy rate, but preimplantation losses were increased. Effects on both pregnancy rates and preimplantation losses were clearly detectable after 28 days, but were of lesser magnitude than after 11 weeks of dosing. Fertility recovered rapidly after dose cessation. These studies illustrate the sensitivity of a long premating dose period at revealing hazard and determining the magnitude of effect on male fertility for compounds that are intended for chronic administration and do not affect testicular histopathology.

Extended one-generation reproductive toxicity study of food-grade titanium dioxide E171 with emphasis on reproductive and endocrine endpoints.

Food-grade titanium dioxide E171 was administered in feed to Sprague Dawley rats in an extended one-generation reproductive toxicity (EOGRT) study (OECD Test 443). The dosed diet (0, 100, 300, or 1000 mg/kg body weight/day) started 10 weeks before mating and continued throughout the study. After weaning, pups were allocated to Cohorts 1 A/1B (to assess reproductive toxicity), 2 A/2B (to assess developmental neurotoxicity), and 3 (to assess developmental immunotoxicity); in addition, Cohort 1B was mated to produce an F2 generation and satellite F0 animals were evaluated for colonic aberrant crypt foci (ACF). In F0 animals, there were no systemic toxicity or reproductive effects, no treatment-related histopathological changes, and no ACF in the colon. Serum estradiol or testosterone concentrations were not changed in F0 or F1 animals. No pre-/postnatal developmental changes related to treatment were noted in F1 animals, and the reproductive performance of F1 Cohort 1B animals was unaffected. F2 pups showed no abnormalities in pre- or postnatal development (postnatal days 4-8). No treatment-related developmental neurotoxicity was observed in Cohorts 2 A/2B. Although no treatment-related immunotoxicity was observed in Cohort 3, the positive control did not induce the expected response; this segment of the study will be repeated. Analyses of blood and urine showed negligible systemic absorption of E171 from the gastrointestinal tract upon dietary ingestion. The no observed adverse effect level (NOAEL) for parental systemic toxicity, reproductive toxicity, offspring toxicity, and developmental neurotoxicity was considered 1000 mg/kg body weight/day. For developmental immunotoxicity, a NOAEL was not determined owing to insufficient T-cell-dependent antibody response in the positive control. Our study provides robust data on the reproductive toxicity and preneoplastic potential of E171.

Update of OECD DART guidelines with endocrine disruptor relevant endpoints: Practical considerations.

In 1998, the OECD initiated a high-priority project aimed at revising existing test guidelines and developing new test guidelines for screening of potential endocrine disruptors. In 2011, OECD 443 was adopted, and in 2015 OECD 421 and OECD 422 were updated with endocrine disruptor relevant endpoints. A feasibility study for the enhancement of OECD 414 with endocrine disruptor relevant endpoints is currently ongoing. The addition of these endpoints is considered crucial for gaining more information on endocrine disruptor potency of tested chemicals, however it should be noted that these additions have a major impact on the study designs and give rise to several practical challenges. The aim of this review is to discuss important aspects of these challenging study designs and to share our knowledge on their implementation in our laboratory. Together, this review can be used as guidance for other laboratories, study monitors and registration officers.