Disposition of glycolic acid into the embryo following oral administration of ethylene glycol during placentation in the rat and rabbit.

In order to evaluate the role of the placenta in the etiology of ethylene glycol (EG) developmental toxicity, the distribution of EG and its main metabolites, glycolic acid (GA) and oxalic acid (OX), into the conceptus was determined at the beginning and completion of placentation in the rat and rabbit. Two groups (n = 28) of timed-pregnant Wistar rats were administered EG (1000 mg/kg bw/day, oral gavage) from gestation day (GD) 6 to either GD 11 or GD 16; similarly, two groups (n = 28) of timed-pregnant New Zealand White rabbits were administered EG from GD 6 to either GD 10 or GD 19. Four animals from each group were sacrificed at 1, 3, 6, 9, 12, 18, or 24 h after the final administration, and maternal blood, extraembryonic fluid, and embryonic tissue were removed for analysis of EG, GA, and OX. The three analytes were predominantly cleared from all compartments in both species within 24 h. Neither EG nor OX preferentially accumulated into the conceptus compartments, compared with the maternal blood, in either species. Critically, GA was preferentially accumulated from the maternal blood only into the rat embryo at GD 11, but not at GD 16 and not into the rabbit embryo at either GD 10 or GD 19. The accumulation of GA into the rat embryo, and its decline over the course of placentation, is discussed in relation to the expression of monocarboxylate transporter isoforms across the syncytiotrophoblast.

Evaluation of an alternative in vitro test battery for detecting reproductive toxicants in a grouping context.

Previously we showed a battery consisting of CALUX transcriptional activation assays, the ReProGlo assay, and the embryonic stem cell test, and zebrafish embryotoxicity assay as 'apical' tests to correctly predict developmental toxicity for 11 out of 12 compounds, and to explain the one false negative [7]. Here we report on applying this battery within the context of grouping and read across, put forward as a potential tool to fill data gaps and avoid animal testing, to distinguish in vivo non- or weak developmental toxicants from potent developmental toxicants within groups of structural analogs. The battery correctly distinguished 2-methylhexanoic acid, monomethyl phthalate, and monobutyltin trichloride as non- or weak developmental toxicants from structurally related developmental toxicants valproic acid, mono-ethylhexyl phthalate, and tributyltin chloride, respectively, and, therefore, holds promise as a biological verification model in grouping and read across approaches. The relevance of toxicokinetic information is indicated.

A high throughput screening system for predicting chemically-induced reproductive organ deformities.

There is a great need for alternative testing methods for reproductive toxicants that are practical, fast, cost-effective and easy to interpret. Previously we followed a pragmatic approach using readily available tests, which was successful in predicting reproductive toxicity of chemicals [13]. This initial battery still contained apical tests and is fairly complex and low in its throughput. The current study aimed to simplify this screening battery using a mechanistic approach and a panel of high throughput CALUX reporter gene assays. A mechanistic approach was taken to validate this high throughput test battery. To this end it was challenged with two preselected sets of chemicals addressing two major apical effect classes relevant in reproductive toxicity. We found selectivity in this battery in that 82% of the compounds inducing reproductive organ deformities were predicted correctly, while for compounds inducing neural tube defects this was the case in 47% only. This is consistent with the mechanisms of toxicity covered in the battery. The most informative assays in the battery were ERalpha CALUX to measure estrogenicity and the AR-anti CALUX assay to measure androgen receptor antagonism.

Delay and impairment in brain development and function in rat offspring after maternal exposure to methylmercury.

Maternal exposure to the neurotoxin methylmercury (MeHg) has been shown to have adverse effects on neural development of the offspring in man. Little is known about the underlying mechanisms by which MeHg affects the developing brain. To explore the neurodevelopmental defects and the underlying mechanism associated with MeHg exposure, the cerebellum and cerebrum of Wistar rat pups were analyzed by [(18)F]FDG PET functional imaging, field potential analysis, and microarray gene expression profiling. Female rat pups were exposed to MeHg via maternal diet during intrauterinal and lactational period (from gestational day 6 to postnatal day (PND)10), and their brain tissues were sampled for the analysis at weaning (PND18-21) and adulthood (PND61-70). The [(18)F]FDG PET imaging and field potential analysis suggested a delay in brain activity and impaired neural function by MeHg. Genome-wide transcriptome analysis substantiated these findings by showing (1) a delay in the onset of gene expression related to neural development, and (2) alterations in pathways related to both structural and functional aspects of nervous system development. The latter included changes in gene expression of developmental regulators, developmental phase-associated genes, small GTPase signaling molecules, and representatives of all processes required for synaptic transmission. These findings were observed at dose levels at which only marginal changes in conventional developmental toxicity endpoints were detected. Therefore, the approaches applied in this study are promising in terms of yielding increased sensitivity compared with classical developmental toxicity tests.

Developmental immunotoxicity of ethanol in an extended one-generation reproductive toxicity study.

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 F(1) 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.

Nasal passages of Göttingen minipigs from the neonatal period to young adult.

Histopathological examination of the nasal passages requires a standardized approach for recording lesion distribution patterns. Nasal diagrams provide guidance to map the lesions. Information on lesions exists for rodents, dogs, and monkeys, which all have been used in inhalation studies. Recently, minipigs have garnered interest as an inhalation model because minipigs resemble humans in many features of anatomy, physiology, and biochemistry and may be a good alternative to monkeys and dogs. The present work explored the microanatomy and histology of the nasal passages of Göttingen minipigs from postnatal day 1 until 6 months of age. Six nasal levels were selected, which allow examination of the squamous, transitional (nonciliated) and ciliated respiratory, and olfactory epithelia; the nasopharynx; and relevant structures such as the vomeronasal organ, olfactory bulb, and nasal/nasopharynx-associated lymphoid tissue.

Developmental immunotoxicity in male rats after juvenile exposure to di-n-octyltin dichloride (DOTC).

To determine relevant endpoints for evaluating developmental immunotoxicity due to juvenile exposure and optimal age of the animals at assessment, a wide range of immunological parameters were assessed in a juvenile toxicity study. Rats were exposed to di-n-octyltin dichloride (DOTC) by gavage from postnatal day (PND) 10 through PND 21 and via the diet after weaning using a benchmark dose (BMD) approach. Immune assessments were performed in male rats on PNDs 21, 42, and 70 and a subset of animals was used to evaluate the T-cell dependent antibody response (TDAR) to Keyhole limpet hemocyanin. Immune effects were more pronounced on PND 21 and 42 and observed at lower doses than developmental effects. The most sensitive immune parameters affected included TDAR parameters and thymocyte subpopulations with lower confidence limits of the benchmark doses (BMDLs) below the overall no-observed-adverse-effect-level (NOAEL) for DOTC reported so far in literature. These findings illustrate the relative sensitivity of the developing immune system for DOTC, the additional value of assessing functional immune parameters, and underscore the relevance of juvenile immunotoxicity testing in view of the risk assessment of chemicals.

Normal anatomy and histology of the adult zebrafish.

The zebrafish has been shown to be an excellent vertebrate model for studying the roles of specific genes and signaling pathways. The sequencing of its genome and the relative ease with which gene modifications can be performed have led to the creation of numerous human disease models that can be used for testing the potential and the toxicity of new pharmaceutical compounds. Many pharmaceutical companies already use the zebrafish for prescreening purposes. So far, the focus has been on ecotoxicity and the effects on embryonic development, but there is a trend to expand the use of the zebrafish with acute, subchronic, and chronic toxicity studies that are currently still carried out with the more conventional test animals such as rodents. However, before we can fully realize the potential of the zebrafish as an animal model for understanding human development, disease, and toxicology, we must first greatly advance our knowledge of normal zebrafish physiology, anatomy, and histology. To further this knowledge, we describe, in the present article, location and histology of the major zebrafish organ systems with a brief description of their function.

Developmental immunotoxicity of di-n-octyltin dichloride (DOTC) in an extended one-generation reproductive toxicity study.

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. F(0) Wistar rats were exposed to DOTC via the feed (0, 3, 10, and 30mg/kg) during pre-mating, mating, gestation and lactation and subsequently F(1) 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 30mg/kg group on PND 42, effects on lymphocyte subpopulations in the spleen were found in the 30mg/kg group on both PNDs 42 and 70. The DTH response already showed an effect at 3mg/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.

Developmental immunotoxicity of methylmercury: the relative sensitivity of developmental and immune parameters.

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.

Comparative reprotoxicity of three oximes.

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.

Effects of cyclosporin A and cyclophosphamide on Peyer's patches in rat, exposed in utero and neonatally or during adult age.

The effects of cyclosporin A (CY) and cyclophosphamide (CPS) on Peyer's patches (PP) were studied in Wistar rats, exposed in utero and neonatally or during adult age. In one study, pregnant dams received 5 or 15 mg/kg bw/day CY from gestation day 6 to day 21 of lactation. In two other studies, animals were exposed at young adult age: female rats received orally 5 or 20 mg/kg/day CY or 5 or 10 mg/kg bw CPS for 4 weeks; males received orally 5 mg/kg bw CPS for 4 weeks, or a single i.v. injection of 50 mg/kg bw CPS. Upon in utero and neonatal exposure, the numbers of grossly observed PP were increased in male pups from the high-dose CY dams at 70 days of age. Exposure to high-dose CY at adult age only tended to decrease the numbers of PP; germinal center development was reduced in the PP from the middle segment of the small intestines, as examined microscopically. Exposure to both doses CPS at adult age reduced the numbers of PP and reduced germinal centre development and the number of lymphocytes in all compartments of PP. It was concluded that the effects of CPS and CY could be established by counting the number of grossly visible PP and by microscopic observation of PP, provided that regional differences of PP were taken into account. Moreover, the type of effects of an immunotoxic agent may vary with age of exposure.