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The susceptibility of developing immune system to chemical disruption warrants the assessment of immune parameters in reproductive and developmental testing protocols. In this study, a wide range of immune endpoints was included in an extended one-generation reproduction toxicity study (EOGRTS) design to determine the relative sensitivity of immune and developmental parameters to ethanol (EtOH), a well-known developmental toxicant with immunomodulatory properties. Adult Wistar rats were exposed to EtOH via drinking water (0, 1.5, 4, 6.5, 9, 11.5 and 14 % (w/v EtOH)) during premating, mating, gestation and lactation and continuation of exposure of the F1 from weaning until killed. Immune assessments were performed at postnatal days (PNDs) 21, 42 and 70. Keyhole limpet hemocyanin (KLH)-specific immune responses were evaluated following subcutaneous immunizations on PNDs 21 and 35. EtOH exposure affected innate as well as adaptive immune responses. The most sensitive immune parameters included white blood cell subpopulations, ConA-stimulated splenocyte proliferation, LPS-induced NO and TNF-α production by adherent splenocytes and KLH-specific immune responses. Most parameters showed recovery after cessation of EtOH exposure after weaning in the 14 % exposure group. However, effects on LPS-induced NO and TNF-α production by adherent splenocytes and KLH-specific parameters persisted until PND 70. The results demonstrate the relative sensitivity to EtOH of especially functional immune parameters and confirm the added value of immune parameters in the EOGRTS. Furthermore, this study identified an expanded KLH-specific parameter set and LPS-induced NO and TNF-α production by adherent splenocytes as valuable parameters that can provide additional information on functional immune effects. © 2012 Springer-Verlag.

Exposure of males to some genotoxic chemicals causes DNA damage in spermatozoa resulting in embryotoxicity and developmental defects in their offspring. This study demonstrates that cisplatin-DNA adducts could be measured in spermatozoa following treatment with the antineoplastic drug, cisplatin. The formation of spermatozoa cisplatin-DNA adducts showed dose and time-dependent increases both in vitro, and in vivo up to 168 h (7 days) after dosing. Treatment of rats with 10 mg cisplatin/kg resulted in spermatozoa Pt-GG adduct levels of approximately 1.0 fmol/μg DNA. When cisplatin-treated male rats were bred to untreated females 6-24 h after cisplatin administration, no adverse developmental effects or decreases in body weight were seen in the offspring although there was a trend towards increased early embryo mortality. (C) 2000 Elsevier Science Ireland Ltd. Chemicals/CAS: Cisplatin, 15663-27-1; cisplatin-DNA adduct; DNA Adducts

Developmental immunotoxicity assessment is considered ready for inclusion in developmental toxicity studies. Further evaluation of proposed and additional assays is needed to determine their utility in assessing developmental immunotoxicity. In this study, a wide range of immunological parameters was included in an extended one-generation reproductive toxicity protocol. F0 Wistar rats were exposed to DOTC via the feed (0, 3, 10, and 30mg/kg) during pre-mating, mating, gestation and lactation and subsequently F1 were exposed from weaning until sacrifice. Immune assessments by several immune parameters were performed at PNDs 21, 42 and 70. The T cell-dependent antibody response to Keyhole Limpet hemocyanin (KLH) was assessed following subcutaneous immunizations with KLH on PNDs 21 and 35 and the delayed-type hypersensitivity response (DTH) against KLH was evaluated at PND 49. No effects were found on PND 21. While effects on lymphocyte subpopulations in the thymus were only observed in the 30. mg/kg group on PND 42, effects on lymphocyte subpopulations in the spleen were found in the 30. mg/kg group on both PNDs 42 and 70. The DTH response already showed an effect at 3. mg/kg and was the overall critical endpoint. The results from this study support the inclusion of splenocyte subpopulation parameters in developmental toxicity studies and identified the DTH response as an important functional parameter. © 2011 Elsevier Ireland Ltd.

Our aim was to investigate a model of the morphologic approach proposed in guidelines for developmental neurotoxicity testing (DNT). Hereto, a limited DNT study [EPA Health Effects Test Guidelines OPPTS 870.6300, 1996a. Developmental Neurotoxicity Study "Public Draft", United States Environmental Protection Agency; Prevention, Pesticides and Toxic Substances (7101); EPA 712-C-96-239, June 1996. http://www.epa.gov/opptsfrs/OPPTS_Harmonized/870_Health_Effects_Test_Guidelines/Drafts/870-6300.pdf was carried out with different doses of methylazoxy methanol acetate (MAM), known to affect brain morphology and neuron numbers in the developing brain. After gross examination, the brains of F1-animals were further dissected along neuro-anatomical landmarks to ensure homology between tissues of different individuals. The (relative) weight of the brain (parts) was determined. One brain half (alternating left/right to avoid lateralization) was further used for microscopic slide reading and measurement of brain layer width (linear morphometry); the other was set aside for stereologic investigation in a later phase of the study. In the offspring, a clear reduction in brain size (gross macroscopy) and weight (MAM high- and top-dose groups) was observed on postnatal days (PN) 22 and 62, but this reduction was hard to pinpoint in the microscope as the changes primarily appeared quantitative in nature, rather than qualitative. Linear measurements of brain layer width appeared very sensitive and efficient. This first step of a project is presented and the perspectives of a further stereologic investigation are discussed. © 2005 Published by Elsevier B.V.

One-generation reproductive toxicity studies have been conducted on the following three oximes: acetaldehyde oxime (AAO), aldecarb oxime (ADO), and methyl isobutyl ketoxime (MIBKO). The studies followed the OECD 415 guideline (One-Generation Reproduction Toxicity Study), with a few modifications. Rats were exposed to the test material for 10 weeks prior to mating and 2 weeks of mating. Males were killed following mating, and females were continuously exposed through gestation and lactation. For MIBKO, the F1 generation was exposed from weaning until approximately 7 weeks of age to include when the vaginal opening occurred in females or when balanopreputial separation occurred in males. With the exception of an increased number of stillbirths in the ADO high-dose-group animals, no adverse effects were observed in any of the reproductive or litter parameters or in the F1 pups. Toxicity to the F0 animals included signs of hemolytic anemia, along with compensatory extramedullary hematopoiesis and hemosiderosis of the spleen. This occurred for all three test materials. For AAO, the no-observed-adverse-effect level (NOAEL) for the F0 generation was considered to be less than 5 mg/kg/day, based on decreased mean corpuscular hemoglobin concentration values and histological changes in the spleen. The NOAEL for the F1 generation and reproductive toxicity was considered to be 50 mg/kg/day, the highest dose tested. For ADO, the NOAEL for parental toxicity was considered to be less than 5 mg/kg/day, based on the histological changes observed in the livers of females in all groups. The NOAEL for reproductive toxicity and the F1 generation was considered to be 25 mg/kg/day, based on the higher number of stillborn pups in the high-dose group. For MIBKO, the NOAEL for parental toxicity was considered to be 30 mg/kg/day, based on the histological effects on the spleen. The NOAEL for the F1 generation and reproductive toxicity was 100 mg/kg/day, the highest dose tested.

To evaluate the ability of a tiered quantitative morphological approach to reveal developmental neurotoxicity, morphometric parameters were measured in the offspring of rats treated with methylazoxymethanol (MAM) during days 13-15 of pregnancy. Treatment was aimed at inhibiting the proliferation phase of hippocampal neurons while leaving cerebellar neurons unaffected. 2D and 3D assessment of brain morphology combined with straightforward measurement of brain size, weight and volume, and the usefulness of estimation of total neuron numbers were studied. Each tier indicated major effects of MAM, from macroscopic effects in the cerebrum (first tier) to a considerable loss of neurons in the hippocampal CA1 pyramidal layer (third tier). The cerebellum and the number of cerebellar granular neurons were not changed. Along with each step of the proposed tiered approach (brain size → linear morphometry → stereology), the discriminative strength of the endpoints, and thus the probability to pinpoint the extent and location of developmental brain lesions increased. © 2005 Elsevier Inc. All rights reserved.

Current developmental and reproductive toxicity protocols include only a limited set of parameters for effects on the developing immune system. In this study, a wide range of immunological parameters were included in a pre- and postnatal developmental toxicity study. Dose-response data were compared to determine the relative sensitivity of different immune and developmental parameters. Mated female Wistar rats were dosed daily by gavage with methylmercury (0, 0.1, 0.4, 0.7, 1.0, 1.5, and 2.0 mg/kg BW/day) from gestational day 6 to postnatal day (PND) 10. In addition to general, reproductive, and developmental parameters, a wide range of immunological parameters were assessed in male offspring at PNDs 21, 42, and 70. The T cell-dependent antibody response to keyhole limpet hemocyanin (KLH) was assessed following sc immunizations on PNDs 21 and 35. Dose-response data were analyzed using the benchmark dose (BMD) approach by fitting dose-response models to the various endpoints. Methylmercury induced effects on developmental parameters, such as growth parameters and pup mortality. Effects on the immune system were found at doses without observed developmental toxicity. Immune effects differed at the three time points and consisted mainly of effects on functional parameters. The parameter with the lowest 5% lower confidence bound of the BMD (BMDL) was the primary KLH-specific IgG antibody response, which showed a dose-dependent decrease with a BMD of 0.039 mg/kg BW/day (CI 0.010-0.12). These data show the relatively high sensitivity of the developing immune system and thereby illustrate the relevance of testing immune parameters in reproductive and developmental toxicity testing protocols. © The Author 2010. Published by Oxford University Press on behalf of the Society of Toxicology. All rights reserved.