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There is a great need for novel in vitro methods to predict human developmental toxicity to comply with the 3R principles and to improve human safety. Human-induced pluripotent stem cells (hiPSC) are ideal for the development of such methods, because they are easy to retrieve by conversion of adult somatic cells and can differentiate into most cell types of the body. Advanced three-dimensional (3D) cultures of these cells, so-called embryoid bodies (EBs), moreover mimic the early developing embryo. We took advantage of this to develop a novel human toxicity assay to predict chemically induced developmental toxicity, which we termed the PluriBeat assay. We employed three different hiPSC lines from male and female donors and a robust microtiter plate-based method to produce EBs. We differentiated the cells into cardiomyocytes and introduced a scoring system for a quantitative readout of the assay—cardiomyocyte contractions in the EBs observed on day 7. Finally, we tested the three compounds thalidomide (2.3–36 µM), valproic acid (25–300 µM), and epoxiconazole (1.3–20 µM) on beating and size of the EBs. We were able to detect the human-specific teratogenicity of thalidomide and found the rodent toxicant epoxiconazole as more potent than thalidomide in our assay. We conclude that the PluriBeat assay is a novel method for predicting chemicals’ adverse effects on embryonic development. Electronic supplementary material The online version of this article (10.1007/s00204-020-02856-6) contains supplementary material, which is available to authorized users.

Exposure of cells or organisms to chemicals can trigger a series of effects at the regulatory pathway level, which involve changes of levels, interactions, and feedback loops of biomolecules of different types. A single-omics technique, e.g., transcriptomics, will detect biomolecules of one type and thus can only capture changes in a small subset of the biological cascade. Therefore, although applying single-omics analyses can lead to the identification of biomarkers for certain exposures, they cannot provide a systemic understanding of toxicity pathways or adverse outcome pathways. Integration of multiple omics data sets promises a substantial improvement in detecting this pathway response to a toxicant, by an increase of information as such and especially by a systemic understanding. Here, we report the findings of a thorough evaluation of the prospects and challenges of multi-omics data integration in toxicological research. We review the availability of such data, discuss options for experimental design, evaluate methods for integration and analysis of multi-omics data, discuss best practices, and identify knowledge gaps. Re-analyzing published data, we demonstrate that multi-omics data integration can considerably improve the confidence in detecting a pathway response. Finally, we argue that more data need to be generated from studies with a multi-omics-focused design, to define which omics layers contribute most to the identification of a pathway response to a toxicant.

Methylmercury (MeHg), an environmental toxicant, induces neuronal cell death and injures a specific area of the brain. MeHg-mediated neurotoxicity is believed to be caused by oxidative stress and endoplasmic reticulum (ER) stress but the mechanism by which those stresses lead to neuronal loss is unclear. Here, by utilizing the ER stress-activated indicator (ERAI) system, we investigated the signaling alterations in the unfolded protein response (UPR) prior to neuronal apoptosis in the mouse brain. In ERAI transgenic mice exposed to MeHg (25 mg/kg, S.C.), the ERAI signal, which indicates activation of the cytoprotective pathway of the UPR, was detected in the brain. Interestingly, detailed ex vivo analysis showed that the ERAI signal was localized predominantly in neurons. Time course analysis of MeHg exposure (30 ppm in drinking water) showed that whereas the ERAI signal was gradually attenuated at the late phase after increasing at the early phase, activation of the apoptotic pathway of the UPR was enhanced in proportion to the exposure time. These results suggest that MeHg induces not only ER stress but also neuronal cell death via a UPR shift. UPR modulation could be a therapeutic target for treating neuropathy caused by electrophiles similar to MeHg.

Exposure to inorganic arsenic (As), a carcinogen and epigenetic toxicant, has been associated with lower circulating levels of insulin-like growth factor 1 (IGF1) and impaired growth in children of pre-school age. The aim of this study was to assess the potential impact of exposure to As on IGF1 and insulin-like growth factor-binding protein 3 (IGFBP3) as well as DNA methylation changes in 9-year-old children. To this end, we studied 9-year-old children from a longitudinal mother–child cohort in rural Bangladesh (n = 551). Prenatal and concurrent exposure to As was assessed via concentrations in maternal urine at gestational week 8 and in child urine at 9 years, measured by HPLC-HG-ICPMS. Plasma IGF1 and IGFBP3 concentrations were quantified with immunoassays. DNA methylation was measured in blood mononuclear cells at 9 years in a sub-sample (n = 113) using the Infinium HumanMethylation450K BeadChip. In multivariable-adjusted linear regression models, prenatal As (natural log-transformed), but not children’s concurrent urinary As, was positively associated with IGFBP3 concentrations (β = 76, 95% CI 19, 133). As concentrations were not associated with IGF1. DNA methylation analysis revealed CpGs associated with both prenatal As and IGFBP3. Mediation analysis suggested that methylation of 12 CpG sites for all children was mediator of effect for the association between prenatal As and IGFBP3. We also found differentially methylated regions, generally hypermethylated, that were associated with both prenatal As and IGFBP3. In all, our study revealed that prenatal exposure to As was positively associated with IGFBP3 concentrations in children at 9 years, independent of IGF1, and this association may, at least in part, be epigenetically mediated. Electronic supplementary material The online version of this article (10.1007/s00204-018-2239-3) contains supplementary material, which is available to authorized users.

The aim of this study was to newly identify and investigate the gender differences in pharmacokinetics (PKs) and tissue distribution of 4-n-nonylphenol (4-n-NP) in both male and female Sprague–Dawley rats. For this study, a UPLC–ESI–MS/MS system for 4-n-NP was developed as a sensitive and rapid analysis method and validated according to the accepted criteria of the international guidelines. The method was finally applied to the analysis of plasma, urine, feces, and nine different tissue samples of rats. PK parameters were calculated after single oral or intravenous administration of 4-n-NP at a dose of 10 or 50 mg/kg. Mean half-life of 4-n-NP in female rats was shorter and its clearance was larger for all doses than those in male rats. There were statistically significant differences in excretion patterns of urine and feces between male and female rats. Distribution of nine different tissues for 4-n-NP was greater in male than in female, and 4-n-NP was highly distributed in the liver or kidney. It was also specific that the distribution of 4-n-NP into brain was considerable. These results suggest that there are gender differences in the PKs of 4-n-NP in rats. Although, 4-n-NP is known to be a reproductive toxicant, reports on its PKs, excretion pattern, tissue distribution, and gender difference are limited. Therefore, our results will be useful data for gender differences as well as toxicokinetic information for 4-n-NP. In addition, it is expected to be very important for future risk assessment and PBPK model establishment of 4-n-NP.

The non-dioxin-like environmental toxicant 2,2',4,4',5,5'-hexachlorobiphenyl (PCB153), member of a group of persistent organic pollutants wide-spread throughout the environment, reduces gap junction intercellular communication (GJIC), an event possibly associated with tumor promotion. Since very few studies have investigated the signaling effectors and mode(s) of action of PCB153, and it is known that the gap junction (GJ) protein Cx43 can be regulated by the bioactive sphingolipid (SL) sphingosine 1-phosphate (S1P), this in vitro study mainly addresses whether SL metabolism is affected by PCB153 in rat liver epithelial WB-F344 cells. PCB153 treatment obtained significant changes in the S1P/ceramide (Cer) ratio, known to be crucial in determining cell fate. In particular, an increase in S1P at 30 min and a decrease of the bioactive lipid at 3 h were observed, whereas Cer level increased at 1 h and 24 h. Notably, a time-dependent modulation of sphingosine kinase (SphK), the enzyme responsible for S1P synthesis, and of its regulators, ERK1/2 and protein phosphatase PP2A, supports the involvement of these signaling effectors in PCB153 toxicity. Electrophysiological analyses, furthermore, indicated that the lipophilic environmental toxicant significantly reduced GJ biophysical properties, affecting both voltage-dependent (such as those formed by Cx43 and/or Cx32) and voltage-independent channels, thereby demonstrating that PCB153 may act differently on GJs formed by distinct Cx isoforms. SphK down-regulation alone induced GJIC impairment, and, when combined with PCB153, the acute effect on GJ suppression was additive. Moreover, after enzyme-specific gene silencing, the SphK1 isoform appears to be responsible for down-regulating Cx43 expression, while being the target of PCB153 at short-term exposure. In conclusion, we provide the first evidence of novel effectors in PCB153 toxic action in rat liver stem-like cells, leading us to consider SLs as potential markers for preventing GJIC deregulation and, thus, the tumorigenic action elicited by this environmental toxicant.

Genomic drift affects the functional properties of cell lines, and the reproducibility of data from in vitro studies. While chromosomal aberrations and mutations in single pivotal genes are well explored, little is known about effects of minor, possibly pleiotropic, genome changes. We addressed this question for the human dopaminergic neuronal precursor cell line LUHMES by comparing two subpopulations (SP) maintained either at the American-Type-Culture-Collection (ATCC) or by the original provider (UKN). Drastic differences in susceptibility towards the specific dopaminergic toxicant 1-methyl-4-phenylpyridinium (MPP+) were observed. Whole-genome sequencing was performed to identify underlying genetic differences. While both SP had normal chromosome structures, they displayed about 70 differences on the level of amino acid changing events. Some of these differences were confirmed biochemically, but none offered a direct explanation for the altered toxicant sensitivity pattern. As second approach, markers known to be relevant for the intended use of the cells were specifically tested. The “ATCC” cells rapidly down-regulated the dopamine-transporter and tyrosine-hydroxylase after differentiation, while “UKN” cells maintained functional levels. As the respective genes were not altered themselves, we conclude that polygenic complex upstream changes can have drastic effects on biochemical features and toxicological responses of relatively similar SP of cells. Electronic supplementary material The online version of this article (10.1007/s00204-018-2326-5) contains supplementary material, which is available to authorized users.

A number of environmental toxicants affect our health through physical, biological or chemical mechanisms. There is growing evidence indicating that microRNA (miRNA) plays an important role in toxicogenomics, disease aetiology and the effect of toxicants. This article summarises recent findings on miRNAs associated with various toxicants and those targeted in the development of therapeutics. Environmental epigenetic studies have revealed the role of miRNAs in the regulation of gene activities induced by environmental changes after exposure to toxic substances. Toxicant-induced changes in miRNA expression have a potential to be informative markers in the evaluation of toxicant risks. miRNAs are now considered to be predictive biomarkers or indicators of tissue injury due to toxicant exposure; thus, miRNAs can also be utilised as therapeutic targets.

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.

The CYP11B1-activated adrenocortical toxicant 3-methylsulphonyl-DDE (3-MeSO2-DDE) is proposed as a lead compound for an improved chemotherapy for adrenocortical carcinoma. We compared the binding of 3-MeSO2-[14C]DDE in the adrenal cortex of four rodent species; hamster, guinea pig, mouse and rat, using a precision-cut adrenal slice culture system ex vivo. Localization and quantification of the bound radioactivity were carried out using light microscopy autoradiography and radioluminography. The results revealed major species differences since 3-MeSO2-[14C]DDE was extensively bound to the hamster adrenal tissue while the guinea pig adrenals were devoid of binding. A high binding in mouse adrenal cortex was confirmed while binding in rat adrenal cortex was very weak. The results support previous observations that metabolic activation of 3-MeSO2-DDE is highly species dependent. Since CYP11B1 could be expressed in tissues other than the adrenal cortex, final toxicological characterization should be carried out in a species that can bioactivate this compound.

The olfactory mucosa (OM) is an important target for metabolism-dependent toxicity of drugs and chemicals. Several OM toxicants share a 2,6-dichlorinated benzene structure. The herbicides dichlobenil (2,6-dichlorobenzonitrile) and chlorthiamide (2,6-dichlorothiobenzamide) and the environmental dichlobenil metabolite 2,6-dichlorobenzamide all induce toxicity in the OM following covalent binding in the Bowman's glands. In addition, we have shown that 2,6-dichlorophenyl methylsulfone targets the Bowman's glands and is probably the most potent OM toxicant so far described. These findings suggest that the 2,6-positioning of chlorines in combination with an electron-withdrawing group in the primary position of the benzene ring is an arrangement that facilitates OM toxicity. This study examined the physicochemical characteristics of the 2,6-dichlorinated OM toxicants. A number of 2,6-dichlorinated benzene derivatives with various types of substituents in primary position were tested for OM toxicity in mice. In addition, some other 2,6- and 2,5-substituted benzene derivatives were examined. Two novel OM toxicants, 2,6-dichlorobenzaldehyde oxime and 2,6-dichloronitrobenzene, were identified. By the use of partial least squares projection to latent structures with discriminant analysis (PLS-DA) a preliminary quantitative structure-activity relationship (QSAR) model was built also using reported OM toxicity data. Physicochemical properties positively correlated with olfactory mucosal toxicity were identified as molecular dipolar momentum and the electronic properties of the substituent. Inversely correlated descriptors were variables describing the hydrophobicity, electronic properties of the molecule such as electron affinity and the electronic charge on the primary carbon. In conclusion, this preliminary PLS-DA model shows that a 2,6-dichlorinated benzene derivative with a large, polar, and strong electron-withdrawing substituent in the primary position has the potential of being a potent OM toxicant in mice.

The current study was designed to determine whether exposure of mice to aerosolized jet fuel (JP8 + 100) resulted in changes in the cellular distribution or immunoreactivity of the enzyme glutathione S-transferase (GST), a biomarker of toxicant exposure. Male mice were exposed to JP8 + 100 at 1000 mg/m3 or 2500 mg/m3 in aerosol for 1 h per day for 7 days and then sacrificed. The retinas were studied by immunohistochemical methods. The JP8 + 100 exposure caused a marked increase in the immunoreactivity of anti-GSTM antibodies with the radial glial cells of the retina, the Müller cells. These results are consistent with the hypothesis that JP8 + 100 acts as a toxicant to mouse retina by permitting the flux of materials across the blood-retina barrier. The findings are relevant to humans because recent studies indicate that Air Force personnel assigned to clean and maintain fuel pods may be exposed to concentrations of JP8 + 100 exceeding 1000 mg/m3.

The aim of this study was to compare results obtained by flow cytometry (FCM) with those obtained from testicular histopathology with regard to testicular damage following acute exposure of adult rats to the known testicular toxicant, methoxyacetic acid (MAA). Special emphasis was given to defining the sensitivity of three-parameter FCM compared with testicular histopathology. Furthermore, the effect on the male reproductive system of a single oral dose of MAA was evaluated with traditional methods, e.g. testicular sperm head counts, and organ weights. Adult, male Han/Wistar rats were randomly assigned to four groups of ten animals to be treated with a single dose of 0, 65, 325 and 650 mg MAA/kg body wt. (p.o., gavage). The animals were killed 2 days after treatment, and testicular and epididymal weights were recorded. One testis and the corresponding epididymis were used for histopathology. The other testis was used partly to determine sonication-resistant, testicular sperm-head counts (SHC), and partly for enzymatic digestion followed by FCM. The results obtained in this study are in agreement with the literature, and show that, in the adult male rat, 2 days after administering a single oral dose of MAA, specific depletion of spermatocytes is evident. Detectable testicular effects were produced by the high (650 mg/kg body wt.) and mid (325 mg/kg body wt.) doses, whilst the low dose (65 mg/kg body wt.) did not produce any noticeable effect. There was a strong correlation between results obtained by FCM and those obtained by testicular histopathology, and no difference in sensitivity between the two methods was observed. In summary, three-parameter FCM represents a sensitive and reliable method for the detection of testicular injury in the rat. It requires only small amounts of tissue, and the sensitivity was shown to be similar to that of histopathology. Moreover, FCM has the advantages of being quick and objective, which permits large numbers of cells to be analysed. The potential use of this method as a fast screening tool for testicular toxicity in routine toxicology studies should be considered.

Labilization of lysosomal enzymes is often associated with the general process of inflammation. The present study investigated the effect of the pneumotoxin cadmium on the release and activity of two lung lysosomal enzymes. Incubation of rat lung lysosomes with cadmium resulted in the release of beta-glucuronidase but not acid phosphatase. The failure to "release" acid phosphatase appears to be the result of a direct inhibitory effect of cadmium on this enzyme. The K1 for cadmium was determined to be 26.3 microM. The differential effect of cadmium on these two lysosomal enzymes suggests that caution should be exercised in selecting the appropriate enzyme marker for assessing lysosomal fragility in the presence of this toxicant. Furthermore, the differential basal release rate of the two enzymes from lung lysosomes may reflect the cellular heterogeneity of the lung.

The effect of the specific muscle toxicant, 2,3,5,6-tetramethyl p-phenylenediamine (TMPD), on urinary creatine and taurine, markers of testicular and liver dysfunction, respectively, has been investigated in male Sprague-Dawley rats. Damage to the gastrocnemius and soleus muscles was accompanied by a rise in serum creatine kinase (predominantly the muscle-specific isoenzyme, CK-MM), alanine aminotransferase (ALT) and aspartate aminotransferase (AST). Increases in serum alpha-hydroxybutyrate dehydrogenase (HBDH) and total lactate dehydrogenase (LDH) (mainly isoenzymes, LDH1 and LDH2), occurred but only minor damage to the heart and no rise in CK-MB, (heart muscle isoenzyme) was seen. Damage to stage XIV tubules in the testis was evident histologically after the highest dose. This was accompanied by an increase in LDH-C4 testis-specific isoenzyme and a decrease in serum testosterone. Apart from reduced serum albumin, no other serum parameters indicated liver damage and there was only slight liver steatosis in some animals at the highest dose. Urinary taurine was not significantly raised after any dose of TMPD, but there was a significant increase in urinary creatine after the highest dose. It can be concluded that in the presence of discrete muscle damage, the use of urinary taurine and urinary creatine as markers of liver and testicular dysfunction, respectively, is not confounded. However, a variety of different markers should be used in conjunction to fully delineate the tissue damage due to toxic chemicals.

Epidemiological and experimental studies have demonstrated the atherogenic effects of environmental toxicant arsenic and fluoride. Inflammatory mechanism plays an important role in the pathogenesis of atherosclerosis. The aim of the present study is to determine the effect of chronic exposure to arsenic and fluoride alone or combined on inflammatory response in rabbit aorta. We analyzed the expression of genes involved in leukocyte adhesion [P-selectin (P-sel) and vascular cell adhesion molecule-1(VCAM-1)], recruitment and transendothelial migration of leukocyte [interleukin-8 (IL-8) and monocyte chemotactic protein-1 (MCP-1)] and those involved in pro-inflammatory cytokines [interleukin-6 (IL-6)]. We found that fluoride and arsenic alone or combined increased the expression of VCAM-1, P-sel, MCP-1, IL-8, and IL-6 at the RNA and protein levels. The gene expressions of inflammatory-related molecules were attenuated when co-exposure to the two toxicants compared with just one of them. We also examined the lipid profile of rabbits exposed to fluoride and (or) arsenic. The results showed that fluoride slightly increased the serum lipids but arsenic decreased serum triglyceride. We showed that inflammatory responses but not lipid metabolic disorder may play a crucial role in the mechanism of the cardiovascular toxicity of arsenic and fluoride.

The environmental pollutant 3-MeSO(2)-DDE [2-(3-methylsulfonyl-4-chlorophenyl)-2-(4-chlorophenyl)-1,1-dichloroethene] is an adrenocortical toxicant in mice, specifically in the glucocorticoid-producing zona fasciculata, due to a cytochrome P450 11B1 (CYP11B1)-catalysed bioactivation and formation of covalently bound protein adducts. o,p'-DDD [2-(2-chlorophenyl)-2-(4-chlorophenyl)-1,1-dichloroethane] is toxic and inhibits steroidogenesis in the human adrenal cortex after bioactivation by unidentified CYPs, but does not exert any toxic effects on the mouse adrenal. As a step towards determining in vitro/in vivo relationships for the CYP-catalysed binding and toxicity of 3-MeSO(2)-DDE and o,p'-DDD, we have investigated the irreversible protein binding of these two toxicants in the murine adrenocortical cell line Y-1. The irreversible binding of 3-MeSO(2)-DDE previously demonstrated in vivo was successfully reproduced and could be inhibited by the CYP-inhibitors etomidate, ketoconazole and metyrapone. Surprisingly, o,p'-DDD reached similar levels of binding as 3-MeSO(2)-DDE. The binding of o,p'-DDD was sensitive to etomidate and ketoconazole, but not to metyrapone. Moreover, GSH depletion increased the binding of 3-MeSO(2)-DDE, but not of o,p'-DDD, indicating an important role of GSH conjugation in the detoxification of the 3-MeSO(2)-DDE-derived reactive metabolite. In addition, the specificity of CYP11B1 in activating 3-MeSO(2)-DDE was investigated using structurally analogous compounds. None of the analogues produced histopathological lesions in the mouse adrenal in vivo following a single i.p. injection of 100 mg/kg body weight, but two of the compounds were able to decrease the irreversible binding of 3-MeSO(2)-DDE to Y-1 cells. These results indicate that the bioactivation of 3-MeSO(2)-DDE by CYP11B1 is highly structure-dependent. In conclusion, both 3-MeSO(2)-DDE and o,p'-DDD bind irreversibly to Y-1 cells despite differences in binding and adrenotoxicity in mice in vivo. This reveals a notable in vitro/in vivo discrepancy, the contributing factors of which remain unexplained. We consider the Y-1 cell line as appropriate for studies of the cellular mechanisms behind the adrenocortical toxicity of these substances.

Cell-specific testicular toxicants have been used to examine the distribution of creatine within the rat testis, and to examine the potential use of creatinuria as a non-invasive indicator of testicular damage. Groups of rats were administered single doses of various toxicants: a germ cell toxicant (methoxyacetic acid, MAA), one of two Sertoli cell toxicants (di-n-pentyl phthalate, DPP or 1,3-dinitrobenzene, 1,3-DNB), or a Leydig cell toxicant (ethane-1,2-dimethane sulphonate, EDS). Urinary creatine and creatinine levels were monitored in 24 h periods over the following 48 h, after which time the testes were removed, weighed and, after processing, sections were examined by light microscopy. All four treatments resulted in reductions in relative testis weight (RTW) and produced morphological changes similar to those which have been previously reported. In addition, MAA, DPP and 1,3-DNB all caused significant elevations in urinary creatine excretion and the urinary creatine: creatinine ratio (Cr/Crn) within 24 h. EDS had no such effect. We conclude that creatine is associated with the cells of the seminiferous epithelium, and that elevated urinary excretion of creatine may serve as a non-invasive marker for damage to these cells in vivo.

The efficacy of DL-dimercaptopropanol (British Anti-Lewisite, BAL), DL-dimercaptopropanesulfonate (DMPS), and meso-dimercaptosuccinic acid (DMSA) was compared in reducing the acute As2O3 toxicity in mice. Mice were treated with a single equimolar dose of a dithiol compound (0.7 mmol/kg i.p.) 0.5 or 30 min after the s.c. injection of various doses of As2O3. Both DMPS and DMSA were significantly (p less than or equal to 0.05) more effective in mice treated 0.5 min after the poisoning if compared to BAL on an equimolar level. The highest potency ratio (PR) (LD50 with treatment/LD50 without treatment) was found in animals injected with DMSA (PR = 8.6). The corresponding value for DMPS was 4.2, and for BAL 2.1, respectively. In animals treated 30 min after poisoning the efficacy of DMPS (PR = 2.6) was similar to the efficacy of DMSA 2.4, both being only slightly superior to BAL 2.0. DMPS and DMSA were found to be much less toxic than BAL. The LD50 of arsenic was 0.057 mmol/kg. The efficacy of BAL, DMPS, and DMSA in reducing the tissue content of arsenic following acute As2O3 poisoning was investigated in mice (n = 6/group) and guinea pigs (n = 3-4/group). The animals were injected s.c. with 0.043 mmol/kg As2O3 (containing a tracer dose of 74As(III)). Thirty minutes later the antidotes were administered i.p. (0.7 mmol/kg). From 2 to 4 h after As2O3 poisoning bile was collected from guinea pigs. Four h after As2O3 injection the content of 74As in blood, liver, kidneys, spleen, heart, lungs, brain, testes, skeletal muscle, and skin in mice and guinea pigs was measured.(ABSTRACT TRUNCATED AT 250 WORDS)

O,O,S-Trimethyl phosphorothioate (OOS-TMP) is an impurity present in a number of widely used organophosphorus insecticides and has been recognized as a potent lung toxicant. OOS-TMP was given p.o. to pregnant rats on gestation day (G) 20 at 0.5, 2.5, 10 and 40 mg/kg. Control dams or pair-fed dams (pair-fed to 40 mg/kg) received 2 ml/kg corn oil. Neonates from treated dams died within 72 h after delivery in a dose-related manner: 100% at 40 mg/kg, 86% at 10 mg/kg, 15% at 2.5 mg/kg, 1% at 0.5 mg/kg, with 3% in controls and 2% in neonates from pair-fed dams. Neonates from treated (40 or 10 mg/kg) and control dams were cross-fostered. The cross-fostering did not affect mortality of neonates from either dosed dams or from control dams. Disposition of OOS-TMP was studied by using [3H]-OOS-TMP at 0.5, 2.5 and 10 mg/kg. Concentrations of OOS-TMP equivalent in fetal lung were about one half of those in mothers at all doses. In another set of experiments, dams (five dams for each dose) were dosed on G 20 with OOS-TMP p.o. at 0, 0.5, 2.5, 10, and 40 mg/kg or pair-fed (pair-fed to 40 mg/kg) and the fetuses were delivered by cesarean section (C-section) on G 23. In neonates from dams dosed with 10 and 40 mg/kg, cyanosis occurred within 4 h after C-section. Histopathological examination revealed dose-related proliferation of type II pneumocytes in dams and proliferation of interstitial cells and delayed septal/capillary development in neonates. However, we could not detect these changes in control fetuses or in fetuses from pair-fed dams. Even at 0.5 mg/kg we found changes in pulmonary morphology in dams and neonates. In other organs such as, liver, brain, spleen, adrenal gland and kidney, we could not detect any morphological changes at 40 mg/kg in either dams or neonates. Thus it was concluded that OOS-TMP caused lung injury in neonates by intrauterine exposure and elicited a lethal response in the neonates.

Ten- and 12-h workdays are relatively common in the chemical and other non-labor intensive industries both in the United States and Europe. Based on pharmacokinetic principles, persons who work 10-12 h shifts and are exposed to chemicals with a terminal half-life between 5 and 200 h will absorb a larger quantity of the toxicant or have higher peak blood levels than persons who work 8-h shifts. To evaluate the effects of exposure duration and repeated exposure on the elimination of carbon tetrachloride (CCl4), rats were repeatedly exposed to 100 ppm 14CCl4 for either 8 or 11.5h/day. Pharmacokinetic equations which describe the plasma concentration and pulmonary elimination during and following single and repeated inhalation exposures were developed. These equations are based on a diffusional type of input function and a linear systems analysis approach. They can be used to make predictions of the cumulation of toxicant following repeated exposure, the relative change in the plasma level following multiple exposures, and the steady-state plasma level based only on the elimination of the chemical in the breath. The pharmacokinetic analysis indicated that rats repeatedly exposed to 100 ppm CCl4 for 11.5 h/day for 4 days per week, or 8 h/day for 5 days per week, will not have increasing plasma levels. The analysis also predicted no significant difference in the peak plasma concentration of CCl4 between the 8 and 11.5h/day schedules following either 1 or 2 weeks of exposure. Due to rapid pulmonary elimination by the rat, the steady state plasma level of CCl4 was reached after only three consecutive exposures for both schedules. The alpha and beta half-lives (X +/- SE) of pulmonary elimination for the 8 h/day group were 84 +/- 9 min and 400 +/- 32 min, respectively. The half-lives for the 11.5 h group were 91 +/- 6 min and 496 +/- 32 min, indicating that the beta phase half-life was significantly longer than that of the 8-h group. This observation, coupled with the tissue distribution data (Paustenbach et al. 1986), suggests that during the longer exposure period a greater fraction of CCl4 is placed in the poorly perfused tissues like fat, thus altering the time-course of elimination in the breath. A general formula for adjusting TLVs for unusually long work schedules is also developed and presented.