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1,3-Dichloropropene (1,3-D) showed a statistically increased incidence of bronchioloalveolar adenomas in male B6C3F1 mice at 60 ppm air concentration during previous chronic inhalation testing. No tumors were observed in female mice, nor in either sex of F344 rats up to 60 ppm, the highest dose tested. Therefore, to understand if lung tumors observed in high dose male mice are due to saturation of metabolic clearance, the linearity of 1,3-D concentrations in mouse blood was investigated on day 15 of repeated nose-only inhalation exposure to 0, 10, 20, 40, 60, 90, and 120 ppm (6 h/d, 7 d/week). Additional groups were included at 20, 60, and 120 ppm for blood collection at 1.5 and 3 h of exposure and up to 25 or 40 min post-exposure to determine area-under-the-curve. The data provide multiple lines of evidence that systemic exposures to 1,3-D in the mouse become nonlinear at inhalation exposure levels of 30 ppm or above. A reduction in minute volume occurred at the highest exposure concentration. The glutathione (GSH)-dependent metabolism of 1,3-D results in significant depletion of GSH at repeated exposure levels of 30 ppm and above. This loss of GSH results in decreased metabolic clearance of this test material, with a concomitant increase of the 1,3-D isomers in circulating blood at exposure concentrations ≥30 ppm. Shifts in the ratio of cis- and trans-1,3-D also support nonlinear toxicokinetics well below 60 ppm. Based on this data, a kinetically derived maximum dose for 1,3-D in mice for repeated exposures should be at or below 30 ppm. These results support non-relevance of 1,3-D-induced benign pulmonary tumorigenicity in mice for human health risk assessment., (© The Author(s) 2019. Published by Oxford University Press on behalf of the Society of Toxicology. All rights reserved. For permissions, please e-mail: journals.permissions@oup.com.)

3-Fucosyllactose (3-FL), a highly abundant complex carbohydrate in human breast milk, functions as a prebiotic promoting early microbial colonization of the gut, increasing pathogen resistance and modulating immune responses. To investigate potential health benefits, 3-FL was produced by fermentation using a genetically modified E. coli K12 strain. The safety assessment of 3-FL included acute oral toxicity, in vitro and in vivo assessment of genetic toxicity, and a subchronic rodent feeding study. 3-FL was not acutely toxic at 5000 mg/kg bw, and there was no evidence of genetic toxicity in the bacterial reverse mutation test and chromosomal aberration assay. There was a repeatable statistically-significant trend in the 4-h S9-activated test conditions in the in vitro micronucleus assay; the confirmatory in vivo mouse micronucleus study was negative at all doses. Dietary subchronic exposure of rats to 3-FL (5% and 10%) did not produce any statistical or biologically-relevant differences in growth, food intake or efficiency, clinical observations, or clinical or anatomic pathology changes at average daily intakes of 5.98 and 7.27 g/kg bw/day for males and females, respectively. The weight of evidence from these studies support the safe use of 3-FL produced using biotechnology as a nutritional ingredient in foods., (Copyright © 2019 Elsevier Ltd. All rights reserved.)

The metabolism and elimination of a xenobiotic has a direct bearing on its potential to cause toxicity in an organism. The confidence with which data from safety studies can be extrapolated to humans depends, among other factors, upon knowing whether humans are systemically exposed to the same chemical entities (i.e. a parent compound and its metabolites) as the laboratory animals used to study toxicity. Ideally, to understand a metabolite in terms of safety, both the chemical structure and the systemic exposure would need to be determined. However, as systemic exposure data (i.e. blood concentration/time data of test material or metabolites) in humans will not be available for agrochemicals, an in vitro approach must be taken. This paper outlines an in vitro experimental approach for evaluating interspecies metabolic comparisons between humans and animal species used in safety studies. The aim is to ensure, where possible, that all potential human metabolites are also present in the species used in the safety studies. If a metabolite is only observed in human in vitro samples and is not present in a metabolic pathway defined in the toxicological species already, the toxicological relevance of this metabolite must be evaluated., (Copyright © 2017 The Authors. Published by Elsevier Inc. All rights reserved.)

The toxicokinetics of 6:2 fluorotelomer alcohol (6:2 FTOH) and its terminal perfluorinated and polyfluorinated metabolites (PFBA, PFHxA, PFHpA and 5:3 Acid) have been calculated from laboratory studies of rats and from a biomonitoring study of humans. In vitro studies with mouse, rat and human hepatocytes indicate qualitatively similar metabolic pathways of 6:2 FTOH. In a one-day inhalation study of 6:2 FTOH in rats, PFBA, PFHxA, PFHpA and 5:3 Acid were determined to be the major metabolites in plasma with calculated elimination half-lives of 1.3-15.4h and metabolic yields up to 2.7 mol%. In five-day and 23-day inhalation studies and a 90-day oral study of 6:2 FTOH, the plasma or serum concentration profile of 5:3 Acid was several-fold higher than concentrations observed in the single day study, resulting in an estimated elimination half-life of 20-30 d. In contrast, the concentrations of PFBA, PFHxA and PFHpA showed little or no concentration increase with repeated exposure. Elimination half-lives of PFHxA, PFHpA and 5:3 Acid in humans were estimated from a study of professional ski wax technicians who were occupationally exposed to aerosolized and volatilized components of fluorinated glide wax. The resulting human elimination half-life values of PFHxA, PFHpA and 5:3 Acid were 32, 70 and 43 d, respectively. Based on a one compartment toxicokinetic model, current environmental air concentrations of 6:2 FTOH are estimated to result in plasma concentrations of PFHxA, PFHpA and 5:3 Acid that are less than or equal to typical LOQ values, in agreement with extant biomonitoring results., (Copyright © 2014 Elsevier Ltd. All rights reserved.)

β-Chloroprene (2-chloro-1,3-butadiene, CD) is used in the manufacture of polychloroprene rubber. Chronic inhalation studies have demonstrated that CD is carcinogenic in B6C3F1 mice and Fischer 344 rats. However, epidemiological studies do not provide compelling evidence for an increased risk of mortality from total cancers of the lung. Differences between the responses observed in animals and humans may be related to differences in toxicokinetics, the metabolism and detoxification of potentially active metabolites, as well as species differences in sensitivity. The purpose of this study was to develop and apply a novel method that combines the results from available physiologically based kinetic (PBK) models for chloroprene with a statistical maximum likelihood approach to test commonality of low-dose risk across species. This method allows for the combined evaluation of human and animal cancer study results to evaluate the difference between predicted risks using both external and internal dose metrics. The method applied to mouse and human CD data supports the hypothesis that a PBK-based metric reconciles the differences in mouse and human low-dose risk estimates and further suggests that, after PBK metric exposure adjustment, humans are equally or less sensitive than mice to low levels of CD exposure., (Copyright © 2014 Elsevier Inc. All rights reserved.)

The framework analysis previously presented for using DNA adduct information in the risk assessment of chemical carcinogens was applied in a series of case studies which place the adduct information into context with the key events in carcinogenesis to determine whether they could be used to support a mutagenic mode of action (MOA) for the examined chemicals. Three data-rich chemicals, aflatoxin B1 (AFB1), tamoxifen (Tam) and vinyl chloride (VCl) were selected for this exercise. These chemicals were selected because they are known human carcinogens and have different characteristics: AFB1 forms a unique adduct and human exposure is through contaminated foods; Tam is a pharmaceutical given to women so that the dose and duration of exposure are known, forms unique adducts in rodents, and has both estrogenic and genotoxic properties; and VCl, to which there is industrial exposure, forms a number of adducts that are identical to endogenous adducts found in unexposed people. All three chemicals produce liver tumors in rats. AFB1 and VCl also produce liver tumors in humans, but Tam induces human uterine tumors, only. To support a mutagenic MOA, the chemical-induced adducts must be characterized, shown to be pro-mutagenic, be present in the tumor target tissue, and produce mutations of the class found in the tumor. The adducts formed by AFB1 and VCl support a mutagenic MOA for their carcinogenicity. However, the data available for Tam shows a mutagenic MOA for liver tumors in rats, but its carcinogenicity in humans is most likely via a different MOA.

β-Chloroprene (2-chloro-1,3-butadiene), a monomer used in the production of neoprene elastomers, is of regulatory interest due to the production of multiorgan tumors in mouse and rat cancer bioassays. A significant increase in female mouse lung tumors was observed at the lowest exposure concentration of 12.8 ppm, whereas a small, but not statistically significant increase was observed in female rats only at the highest exposure concentration of 80 ppm. The metabolism of chloroprene results in the generation of reactive epoxides, and the rate of overall chloroprene metabolism is highly species dependent. To identify potential key events in the mode of action of chloroprene lung tumorigenesis, dose-response and time-course gene expression microarray measurements were made in the lungs of female mice and female rats. The gene expression changes were analyzed using both a traditional ANOVA approach followed by pathway enrichment analysis and a pathway-based benchmark dose (BMD) analysis approach. Pathways related to glutathione biosynthesis and metabolism were the primary pathways consistent with cross-species differences in tumor incidence. Transcriptional BMD values for the pathway were more similar to differences in tumor response than were estimated target tissue dose surrogates based on the total amount of chloroprene metabolized per unit mass of lung tissue per day. The closer correspondence of the transcriptional changes with the tumor response is likely due to their reflection of the overall balance between metabolic activation and detoxication reactions, whereas the current tissue dose surrogate reflects only oxidative metabolism.

β-Chloroprene (chloroprene) is carcinogenic in inhalation bioassays with B6C3F1 mice and Fischer rats, but the potential effects in humans have not been adequately characterized. In order to provide a better basis for evaluating chloroprene exposures and potential effects in humans, we have explored species and tissue differences in chloroprene metabolism. This study implemented an in vitro-in vivo extrapolation (IVIVE) approach to parameterize a physiologically based pharmacokinetic (PBPK) model for chloroprene and evaluate the influence of species and gender differences in metabolism on target tissue dosimetry. Chloroprene metabolism was determined in vitro using liver, lung and kidney microsomes from male or female mice, rats, and humans. A two compartment PK model was used to estimate metabolism parameters for chloroprene in an in vitro closed vial system, which were then extrapolated to the whole body PBPK model. Two different strategies were used to estimate parameters for the oxidative metabolism of chloroprene: a deterministic point-estimation using the Nelder-Mead nonlinear optimization algorithm and probabilistic Bayesian analysis using the Markov Chain Monte Carlo technique. Target tissue dosimetry (average amount of chloroprene metabolized in lung per day) was simulated with the PBPK model using the in vitro-based metabolism parameters. The model-predicted target tissue dosimetry, as a surrogate for a risk estimate, was similar between the two approaches; however, the latter approach provided a measure of uncertainty in the metabolism parameters and the opportunity to evaluate the impact of that uncertainty on predicted risk estimates., (Copyright © 2012 Elsevier Ltd. All rights reserved.)

8:2 fluorotelomer alcohol (8:2 FTOH) inhalation exposure was investigated to (1) compare plasma metabolites to oral data, (2) conduct a route-to-route extrapolation (oral to inhalation), (3) develop a human equivalent air concentration (HEC) from a 90-day oral sub-chronic study in rats using BMD analysis, and (4) calculate a margin of exposure (MOE) between the HEC and measured air concentrations. Male and female rats were exposed nose-only for 6h at 3 or 30mg/m(3). Blood was collected at 1, 3 and 6h during exposure and 6 and 18h post exposure. Alcohol, perfluorocarboxylic acid and polyfluorinated acid metabolites were determined in plasma by LC-MS/MS. 8:2 FTOH was

In vitro metabolism of 1,2,3,3,3-pentafluoropropene (PFP) was investigated in the present study. PFP was metabolized via cytochrome P450-catalyzed oxidative dehalogenation in liver microsomes and glutathione transferase (GST)-catalyzed conjugation in liver microsomes and cytosol. Two oxidation products, 2,3,3,3-tetrafluoropropionaldehyde (TPA) and 3,3,3-trifluoropyruvaldehyde (TFPA), and two GSH conjugates, S-(2,3,3,3-tetrafluoropropenyl)-GSH (TFPG) and S-(1,2,3,3,3-pentafluoropropyl)-GSH (PFPG) were identified. Enzyme kinetic parameters for the formation of TFPA, TFPG, and PFPG were obtained in male and female rat, mouse, dog, and human liver microsomes and cytosol and were confirmed using freshly isolated male rat hepatocytes. For the TFPA pathway, dog microsomes exhibited much larger K(m) values than rat, mouse, and human microsomes. Sex differences in the rates of metabolism within a given species were minor and generally were less than 2-fold. Across the species, liver microsomes were the primary subcellular fraction for GSH S-conjugation and the apparent reaction rates for the formation of TFPG were much greater than those for PFPG in liver microsomes. PFPG was unstable and had a half-life of approximately 3.9 h in a phosphate buffer (pH 7.4 and 37°C). The intrinsic clearance values for the formation of TFPA were much greater than those for the formation of GSH S-conjugates, suggesting that cytochrome P450-mediated oxidation is the primary pathway for the metabolism of PFP at relatively low PFP concentrations. Because saturation of the GST-mediated reactions was not reached at the highest possible PFP concentration, GSH S-conjugation may become a much more important pathway at higher PFP concentrations (relative to the K(m) for TFPA).

We developed and validated an ion chromatography method to assay iodide in serum sampled from rats and rabbits that had been exposed to iodomethane. Iodomethane is of interest because it is a volatile liquid pre-plant soil crop protection fumigant that has been proposed as a non-ozone-depleting alternative to methyl bromide. Serum was prepared from whole blood collected on wet ice at the time of sacrifice and kept frozen at less than -65 degrees C. For analysis, serum samples were thawed unassisted at ambient temperature. Proteins were separated from the serum samples by ultrafiltration. A 100-microl filtered serum sample was then injected into the ion chromatograph without additional sample preparation. Iodide was separated in <20 min by anion-exchange chromatography using a 25-mM nitric acid eluent. The analyte of interest was detected by pulsed amperometry using a silver working electrode. The method showed linear response over the concentration range of 100 to 5000 ng/ml iodide (r2>.998) with a lower limit of quantitation of 100 ng/ml iodide. The accuracy of the procedure, determined by spiked recovery measurements at 100 ng/ml iodide, was between 90 and 110%. A method detection limit of 20 ng/ml for iodide in serum samples was demonstrated using the method of standard additions.

Laboratory animals exposed to methyl iodide (MeI) have previously demonstrated lesions of the olfactory epithelium that were associated with local metabolism in the nasal tissues. Interactions of MeI in the nasal passage may, therefore, alter systemic toxicokinetics. The current study used unrestrained plethysmographs to determine the MeI effect on the breathing frequency and minute volume (MV) in rats and rabbits. Groups of 4 rats each were exposed to 0, 25, or 100 ppm and groups of 4 rabbits each were exposed to 0 and 20 ppm MeI for 6 h. Breathing frequency and MV were measured and recorded during the exposure. Blood samples were collected for inorganic serum iodide and the globin adduct S-methylcysteine (SMC) as biomarkers of systemic kinetics immediately following exposure. No significant reductions in breathing frequency were observed for either rats or rabbits. Significant changes in minute volume were demonstrated by both rats and rabbits; however, the changes observed in rats were not concentration dependent. The MeI-induced changes in MV resulted in significant differences in the total volume of test substance atmosphere inhaled over the 6-h period. Rats demonstrated a concentration-dependent increase in both inorganic serum iodide and SMC. Rabbits exposed to 20 ppm MeI demonstrated a significant increase of inorganic serum iodide; SMC was also increased but was not statistically significant. The results of this study are consistent with previous kinetic studies with MeI, and the data presented here can be integrated into a computational fluid dynamics physiologically based pharmacokinetic model for both rats and rabbits.

The effects of inhaled methyl iodide (MeI) on clinical pathology parameters, glutathione (GSH) tissue levels, serum thyroid hormone and inorganic iodide concentrations, S-methylcysteine hemoglobin concentrations, and liver UDP-glucuronyltransferase activity were studied in the rat. Male rats were exposed by whole-body inhalation to 0, 25, or 100 ppm MeI, 6 h/day for up to 2 days. Serum cholesterol concentrations (both high-density lipoprotein [HDL] and low-density lipoprotein [LDL] fractions) were increased and triglycerides were decreased at both exposure levels. Serum thyroid-stimulating hormone (TSH) concentrations were increased at 25 and 100 ppm, and serum triiodothyronine (T(3)) and thyroxine (T(4)) concentrations were decreased at 100 ppm. There was no change in either reverse triiodothyronine (rT(3)) or UDP-glucuronyltransferase activity at either exposure level. A dose- and time-dependent reduction in GSH levels in blood, kidney, liver, and nasal tissue was observed, with the greatest reduction in nasal tissue (olfactory and respiratory epithelium). MeI exposure also resulted in a substantial dose- and time-dependent increase in both serum inorganic iodide and red blood cell S-methylcysteine hemoglobin adducts. These results indicate that following inhalation exposure, MeI is rapidly metabolized in blood and tissue of rats, resulting in methylation products and release of inorganic iodide.

The formation of deoxyribonucleic acid (DNA) adducts can have important and adverse consequences for cellular and whole organism function. Available methods for identification of DNA damage and quantification of adducts are reviewed. Analyses can be performed on various samples including tissues, isolated cells, and intact or hydrolyzed (digested) DNA from a variety of biological samples of interest for monitoring in humans. Sensitivity and specificity are considered key factors for selecting the type of method for assessing DNA perturbation. The amount of DNA needed for analysis is dependent upon the method and ranges widely, from <1 microg to 3 mg. The methods discussed include the Comet assay, the ligation-mediated polymerase reaction, histochemical and immunologic methods, radiolabeled ((14)C- and (3)H-) binding, (32)P-postlabeling, and methods dependent on gas chromatography (GC) or high-performance liquid chromatography (HPLC) with detection by electron capture, electrochemical detection, single or tandem mass spectrometry, or accelerator mass spectrometry. Sensitivity is ranked, and ranges from approximately 1 adduct in 10(4) to 10(12) nucleotides. A brief overview of oxidatively generated DNA damage is also presented. Assay limitations are discussed along with issues that may have impact on the reliability of results, such as sample collection, processing, and storage. Although certain methodologies are mature, improving technology will continue to enhance the specificity and sensitivity of adduct analysis. Because limited guidance and recommendations exist for adduct analysis, this effort supports the HESI Committee goal of developing a framework for use of DNA adduct data in risk assessment.

Chloroethane was observed in a chronic cancer bioassay to be a mouse-specific uterine carcinogen at a single high inhaled concentration (15,000 ppm). Although high incidence occurred in the female mouse (86%), no uterine tumor increases were observed in female rats. Chloroethane is a weak alkylating agent and has low acute toxicity. No genotoxicity potential has been observed below 40,000 ppm. Chloroethane is eliminated from the body by pulmonary exhalation and metabolically by oxidation via cytochrome P-450 (likely producing acetaldehyde) and conjugation with glutathione (GSH). The mode of action for the mouse-specific uterine tumors is not definitively known and could involve parent chemical and/or metabolite(s). A physiologically based pharmacokinetic (PBPK) model for chloroethane disposition in the rat was developed previously, but no such models have been described for mice or humans. For the work reported here, the existing PBPK model for chloroethane in rats was expanded and refined, and PBPK models for chloroethane disposition in mice and humans were developed to allow species comparisons of internal dosimetry and for possible insights into the carcinogenic mode of action. The amounts metabolized via glutathione-S-transferase (GST) versus cytochrome P-450, and the total amount of chloroethane absorbed, were most consistent with the observations made concerning uterine tumors, with amounts metabolized via GST providing the larger quantitative difference between the two rodent species. Choice of the most relevant dose metric for risk assessments involving uterine tumors in mice will require pharmacodynamic considerations in the mode of action in addition to the pharmacokinetic differences reported here.

The detection of perfluorinated organic compounds in the environment has generated interest in their biological fate. 8-2 Fluorotelomer alcohol (8-2 FTOH, C(7)F(15)CF(2)CH(2)CH(2)OH), a raw material used in the manufacture of fluorotelomer-based products, has been identified in the environment and has been implicated as a potential source for perfluorooctanoic acid (PFOA) in the environment. In this study, the in vitro metabolism of [3-(14)C] 8-2 FTOH and selected acid metabolites by rat, mouse, trout, and human hepatocytes and by rat, mouse, and human liver microsomes and cytosol were investigated. Clearance rates of 8-2 FTOH in hepatocytes indicated rat > mouse > human >/= trout. A number of metabolites not previously reported were identified, adding further understanding to the pathway for 8-2 FTOH metabolism. Neither perfluorooctanoate nor perfluorononanoate was detected from incubations with human microsomes. To further elucidate the steps in the metabolic pathway, hepatocytes were incubated with 8-2 fluorotelomer acid, 8-2 fluorotelomer unsaturated acid, 7-3 acid, 7-3 unsaturated acid, and 7-2 secondary fluorotelomer alcohol. Shorter chain perfluorinated acids were only observed in hepatocyte and microsome incubations of the 8-2 acids but not from the 7-3 acids. Overall, the results indicate that 8-2 FTOH is extensively metabolized in rats and mice and to a lesser extent in humans and trout. Metabolism of 8-2 FTOH to perfluorinated acids was extremely small and likely mediated by enzymes in the microsomal fraction. These results suggest that human exposure to 8-2 FTOH is not expected to be a significant source of PFOA or any other perfluorocarboxylic acids.

beta-Chloroprene (2-chloro-1,3-butadiene; CD), which is used in the synthesis of polychloroprene, caused significant incidences of several tumor types in B6C3F1 mice and Fischer rats, but not in Wistar rats or Syrian hamsters. This project investigates the relevance of the bioassay lung tumor findings to human health risk by developing a physiologically based toxicokinetic (PBTK) model and exploring a tissue specific exposure-dose-response relationship. Key steps included identification of the plausible genotoxic mode of action, experimental quantification of tissue-to-air partition coefficients, scaling of in vitro parameters of CD metabolism for input into the PBTK model, comparing the model with in vivo experimental gas uptake data, selecting an appropriate tissue dosimetric, and predicting a corresponding human exposure concentration. The total daily milligram amount of CD metabolized per gram of lung was compared with the animal bioassay response data, specifically combined bronchiolar adenoma/carcinoma. The faster rate of metabolism in mouse lung agreed with the markedly greater incidence of lung tumors compared with the other rodent species. A lung tissue dose was predicted for the combined rodent lung tumor bioassay data at a 10% benchmark response. A human version of the PBTK model predicted that the lung tissue dose in humans would be equivalent to continuous lifetime daily exposure of 23 ppm CD. PBTK model sensitivity analysis indicated greater dependence of model predictions of dosimetry on physiological than biochemical parameters. The combined analysis of lung tumor response across species using the PBTK-derived internal dose provides an improved alternative to default pharmacokinetic interspecies adjustments for application to human health risk assessment.

Beta-chloroprene (2-chloro-1,3-butadiene, CD) is carcinogenic by inhalation exposure to B6C3F1 mice and Fischer F344 rats but not to Wistar rats or Syrian hamsters. The initial step in metabolism is oxidation, forming a stable epoxide (1-chloroethenyl)oxirane (1-CEO), a genotoxicant that might be involved in rodent tumorigenicity. This study investigated the species-dependent in vitro kinetics of CD oxidation and subsequent 1-CEO metabolism by microsomal epoxide hydrolase and cytosolic glutathione S-transferases in liver and lung, tissues that are prone to tumor induction. Estimates for Vmax and Km for cytochrome P450-dependent oxidation of CD in liver microsomes ranged from 0.068 to 0.29 micromol/h/mg protein and 0.53 to 1.33 microM, respectively. Oxidation (Vmax/Km) of CD in liver was slightly faster in the mouse and hamster than in rats or humans. In lung microsomes, Vmax/Km was much greater for mice compared with the other species. The Vmax and Km estimates for microsomal epoxide hydrolase activity toward 1-CEO ranged from 0.11 to 3.66 micromol/h/mg protein and 20.9 to 187.6 microM, respectively, across tissues and species. Hydrolysis (Vmax/Km) of 1-CEO in liver and lung microsomes was faster for the human and hamster than for rat or mouse. The Vmax/Km in liver was 3 to 11 times greater than in lung. 1-CEO formation from CD was measured in liver microsomes and was estimated to be 2-5% of the total CD oxidation. Glutathione S-transferase-mediated metabolism of 1-CEO in cytosolic tissue fractions was described as a pseudo-second order reaction; rates were 0.0016-0.0068/h/mg cytosolic protein in liver and 0.00056-0.0022 h/mg in lung. The observed differences in metabolism are relevant to understanding species differences in sensitivity to CD-induced liver and lung tumorigenicity.

The estimation and characterization of a cancer risk is grounded in the observation of tumors in humans and/or experimental animals. Increasingly, however, other kinds of data (non-tumor data) are finding application in cancer risk assessment. Metabolism and kinetics, adduct formation, genetic damage, mode of action, and biomarkers of exposure, susceptibility, and effects are examples. While these and other parameters have been studied for many important chemicals over the past 30-40 years, their use in risk assessments is more recent, and new insights and opportunities are continuing to unfold. To provide some perspective on this field, the ILSI Risk Science Institute asked a select working group to characterize the pertinent non-tumor data available for 1,3-butadiene, benzene, and vinyl chloride and to comment on the utility of these data in characterizing cancer risks. This paper presents the findings of that working group and concludes with 15 simple principles for the use of non-tumor data in cancer risk assessment., (Copyright 2003 Elsevier Science (USA))

beta-Chloroprene (CD), the 2-chloro derivative of 1,3-butadiene, is used for the manufacture of the synthetic rubber, polychloroprene. Acute inhalation studies show that CD is lethal to Crl:CD rats at >2300 p.p.m. (4 h); the primary target organ effects were pulmonary hemorrhage and edema, and hepatic necrosis. In 2- and 4-week inhalation studies in Fischer 344 (F344) and Wistar rats, early deaths occurred at 500 and > or =161 p.p.m., respectively. Organ system injury was found in the nose (degeneration/metaplasia of olfactory epithelium), liver (centrilobular necrosis), and blood (decreased red blood cell count in F344 rats only). In a 90-day inhalation study with F344 rats, degeneration/metaplasia of the olfactory epithelium and reduced nonprotein sulfhydryl content of lungs and liver were found in animals exposed to 80 p.p.m., and anemia, hepatocellular necrosis, and forestomach inflammation were observed at 200 p.p.m. In a 90-day study with B6C3F1 mice, CD caused deaths at 200 p.p.m., the highest concentration tested, and epithelial hyperplasia of the forestomach at 80 p.p.m. Other than a slight (<10%) reduction in sperm motility in male rats at 200 p.p.m., all other reproductive parameters (sperm count or morphology in males, and estrous cyclicity or cycle length in females) were unaffected in these 90-day rat/mouse studies. There were no significant indications of neurological toxicity. The study No-Observable Adverse Effect Level was 32 p.p.m. based on nasal injury in rats. Despite some early reports of reproductive system abnormalities at levels <1 p.p.m., recent studies show no embryotoxic or developmental toxicity in female Wistar or Crl:CD rats, or in New Zealand White rabbits at CD exposure concentrations up to 25 or 175 p.p.m., respectively. In a one-generation reproduction study with Wistar rats, CD produced growth retardation in the F(0) generation exposed to 100 p.p.m., and in the F(1) offspring at 33 and 100 p.p.m.; no effects on reproductive parameters or histopathology were found. CD is nonmutagenic in standard plate incorporation bacterial reverse mutation assays (Ames assays) but positive using direct gas-phase incubation methods. Bacterial mutagenicity (primarily base pair substitution) was either negative or weakly positive when freshly prepared CD was tested. Mutagenicity increased markedly with time, presumably from CD dimer formation, and also by addition of liver S9 metabolic activation system. In vivo micronucleus, chromosome aberration and sister chromatid exchange studies in mice showed no structural chromosomal damage. Overall, the pathological effects in the liver and nose dominate the subchronic toxicity of CD. The genotoxicity of CD is inconsistent and requires further study.

Based on analogy with butadiene and isoprene, the metabolism of beta-chloroprene (2-chloro-1,3-butadiene, CD) to reactive intermediates is likely to be a key determinant of tumor development in laboratory rodents exposed to CD by inhalation. The purpose of this study is to identify species differences in toxic metabolite (epoxide) formation and detoxification in rodents and humans. The in-vitro metabolism of CD was studied in liver microsomes of B6C3F1 mice, Fischer/344 and Wistar rats, Syrian hamsters, and humans. Microsomal oxidation of CD in the presence of NADP(+), extraction with diethyl ether, and analysis by GC-mass selective detection (MSD) indicated that (1-chloroethenyl)oxirane (CEO) was an important metabolite of CD in the liver microsomal suspensions of all species studied. Other potential water-soluble oxidative metabolites may have been present. The oxidation of CD was inhibited by 4-methyl pyrazole, an inhibitor of CYP 2E1. CEO was sufficiently volatile at 37 degrees C for vial headspace analysis using GC-MSD single ion monitoring (m/z=39). CEO was synthesized and used to conduct partition measurements along with CD and further explore CEO metabolism in liver microsomes and cytosol. The liquid-to-air partition coefficients for CD and CEO in the microsomal suspensions were 0.7 and 58, respectively. Apparent species differences in the uptake of CEO by microsomal hydrolysis were hamster approximately human>rats>mice. Hydrolysis was inhibited by 1,1,1-trichloropropene oxide, a competitive inhibitor of epoxide hydrolase. A preliminary experiment indicated that the uptake of CEO in liver cytosol by GSH conjugation was hamster>rats approximately mice (human cytosol not yet tested). In general, the results suggest that metabolism may help explain species differences showing a greater sensitivity for CD-induced tumorigenicity in mice, for example, compared with hamsters. Additional experiments are in progress to quantify the kinetic parameters of CD oxidation and CEO metabolism by enzymatic hydrolysis and conjugation by glutathione S-transferase for in cytosol. A future goal is to use the kinetic rates to parameterize a physiologically based toxicokinetic model and relate the burden of toxic metabolite to the cancer dose-response observed in experimental animals.

Potential health effects of human exposure to 1,3-butadiene (BD) are of concern due to the use of BD in industry and its low-level presence throughout the environment. Physiologically based toxicokinetic (PBTK) models of BD in rodents have been developed by multiple research groups in an effort to explain species differences in toxicity (especially carcinogenic potency) through toxicokinetics. PBTK modeling of dose metrics related to a non-cancer endpoint, ovotoxicity in experimental animals, was conducted. The cumulative area under the blood concentration vs. time curve (AUC) for the metabolite diepoxybutane (butadiene diepoxide, DEB) was found to be consistent with ovotoxicity in mice and rats exposed to BD by inhalation or epoxybutene (butadiene monoepoxide, EB) or DEB by intraperitoneal injection. This suggests that cumulative DEB AUC may also be an appropriate metric for possible human risk. A preliminary human PBTK model was assembled for the eventual assessment of reproductive risk to humans and for prioritizing the determination of model parameters. The preliminary model accurately predicted published data on exhaled breath BD concentrations in a human volunteer exposed to BD by inhalation. The fit was relatively insensitive to the rate constant for BD epoxidation. Sensitivity analyses were conducted on this human PBTK model. Using a range of published rate constants, human blood DEB was found to be sensitive to rates of epoxidation of EB to DEB and hydrolysis of EB and DEB, but not BD epoxidation. Because of the large ranges of rates measured in vitro for these reactions, different combinations of in-vitro rates produce varying predictions of blood DEB concentration. Thus, validation of a human PBTK model with human biomonitoring data will be essential to produce a PBTK model that can be applied to risk assessment.

(1-Chloroethenyl)oxirane (CEO) is a metabolite of beta-chloroprene (2-chloro-1,3-butadiene, CD). The purpose of this study was to evaluate the in vitro mutagenic and clastogenic (chromosome breaking) potential of CEO. For comparative purposes, the study also included an evaluation of the racemic compounds, 3,4-epoxy-1-butene (EB) and 1,2:3,4-diepoxybutane (DEB). Mutagenicity was evaluated in a bacterial reverse mutation test (Ames), using the pre-incubation method in the presence and absence of an exogenous metabolism system (Aroclor)-induced rat liver S9). Four Salmonella typhimurium tester strains, TA97a, TA98, TA100 and TA1535 were used. The exposure concentrations in the sealed incubation vials ranged from 0 to 69 mM for CEO, 0 to 102 mM for EB, and 0 to 83 mM for DEB. All three compounds showed signs of toxicity, with DEB being substantially more toxic than either CEO or EB. Mutagenic activity was observed with all three chemicals in primarily the base pair substitution strains (S. typhimurium TA100 and TA1535), but some activity was also seen in the frameshift elimination strains (S. typhimurium TA97a and TA98). The observed mutagenic responses after exposure with CEO or EB were greater than the observed response for DEB, most likely because of the higher toxicity of DEB. Generally, the mutagenic responses were unchanged in the frameshift strains and base pair substitution strains in the presence of S9 metabolism. In vitro clastogenicity was evaluated using the cytochalasin-B blocked micronucleus test in cultured Chinese hamster V79 cells. The test was conducted without S9 metabolism because of the absence of substantial changes in the Ames test. Exposure concentrations ranged from 0 to 0.943 mM for CEO, 0 to 3.0 mM for EB, and 0 to 0.035 mM for DEB, with the upper exposure concentrations dictated by cytotoxicity. Cytotoxicity, measured as a reduction in the proportion of binucleated cells and altered cell morphology, was observed for CEO at concentrations > or =0.175 mM. Exposure to EB led to a reduced proportion of binucleated cells at concentrations > or =2.0 mM, and cell death was observed after DEB exposure at concentrations > or =0.025 mM. No clastogenicity was observed in the V79 cells when tested up to cytotoxic concentrations of CEO, whereas an elevated frequency of micronuclei was observed after exposure to either EB (> or =1.0 mM) or DEB (> or =0.0125 mM). These results suggest that CEO-induced mutagenicity, but not clastogenicity, may contribute to the observed beta-chloroprene-induced carcinogenicity in the rodent bioassay studies.

Benzene (BZ) requires oxidative metabolism catalyzed by cytochrome P-450 2E1 (CYP 2E1) to exert its hematotoxic and genotoxic effects. We previously reported that male mice have a two-fold higher maximum rate of BZ oxidation compared with female mice; this correlates with the greater sensitivity of males to the genotoxic effects of BZ as measured by micronuclei induction and sister chromatid exchanges. The aim of this study was to quantitate levels of BZ metabolites in urine and tissues, and to determine whether the higher maximum rate of BZ oxidation in male mice would be reflected in higher levels of hydroxylated BZ metabolites in tissues and water-soluble metabolites in urine. Male and female B6C3F, mice were exposed to 100 or 600 ppm 14C-BZ by nose-only inhalation for 6 h. An additional group of male mice was pretreated with 1% acetone in drinking water for 8 d prior to exposure to 600 ppm BZ; this group was used to evaluate the effect of induction of CYP 2E1 on urine and tissue levels of BZ and its hydroxylated metabolites. BZ, phenol (PHE), and hydroquinone (HQ) were quantified in blood, liver, and bone marrow during exposure and postexposure, and water-soluble metabolites were analyzed in urine in the 48 h after exposure. Male mice exhibited a higher flux of BZ metabolism through the HQ pathway compared with females after exposure to either 100 ppm BZ (32.0 2.03 vs. 19.8 2.7%) or 600 ppm BZ (14.7 1.42 vs. 7.94 + 0.76%). Acetone pretreatment to induce CYP 2E1 resulted in a significant increase in both the percent and mass of urinary HQ glucuronide and muconic acid in male mice exposed to 600 ppm BZ. This increase was paralleled by three- to fourfold higher steady-state concentrations of PHE and HQ in blood and bone marrow of acetone-pretreated mice compared with untreated mice. These results indicate that the higher maximum rate of BZ metabolism in male mice is paralleled by a greater proportion of the total flux of BZ through the pathway for HQ formation, suggesting that the metabolites formed along this pathway may be responsible for the genotoxicity observed following BZ exposure.

In vitro and in vivo butadiene (BD) metabolism data from laboratory animals were integrated into a rodent physiologically based pharmacokinetic (PBPK) model with flow- and diffusion-limited compartments. The resulting model describes experimental data from multiple sources under scenarios such as closed chamber inhalation and nose-only flow-through inhalation exposures. Incorporation of diurnal glutathione (GSH) variation allows accurate simulation of GSH changes observed in air control nose-only exposures and BD exposures. An isolated tissue model based on rate parameters determined in vitro predicts the decrease in epoxide concentrations in intact animals during the time lag between exsanguination and tissue removal for tissues capable of epoxide biotransformation, providing a better indication of in vivo dosimetry. Further refinements of the model are required relative to model predictions of an important BD metabolite, diepoxybutane.

Significant species differences exist in the susceptibility to butadiene (BD)-induced cancer in rats and mice, and metabolism is likely a critical determinant for species sensitivity. This study measured the in vivo concentrations of, (1) BD in blood; (2) epoxybutene (EB) and diepoxybutane (DEB) in blood, lung and liver; and (3) glutathione (GSH) in lung and liver of male B6C3F1 mice and Sprague-Dawley rats during and after 6-h exposure to 62.5, 625, 1250, and 8000 (rat only) ppm BD. Mice had higher concentrations of EB and DEB in blood and tissues than did rats, DEB could not be detected in blood or tissues of rats, and the greatest depletion of GSH occurred in the lungs of mice. During exposure, the peak concentrations of EB in mice compared with rats were 4- to 8-fold higher in blood, 13- to 15-fold higher in lung, and 5- to 8-fold higher in liver. These data suggest that higher levels of BD epoxides in blood and tissues of mice compared with rats may explain, in part, the greater sensitivity of mice than rats to BD-induced carcinogenicity.

1,3-Butadiene is a carcinogen in rats and mice, with mice being substantially more sensitive than rats. Our recent research is directed toward obtaining a better understanding of the cancer risk of butadiene in humans by evaluating species-dependent differences in the formation of the toxic metabolites epoxybutene and diepoxybutane. The recent data include in vitro studies on butadiene metabolism using tissues from humans, rats, and mice as well as experimental data and physiological model predictions for butadiene in blood and butadiene epoxides in blood, lung, and liver after exposure of rats and mice to inhaled butadiene. The findings suggest that humans would be more like rats and less like mice regarding the formation of butadiene epoxides. These research findings permit a reassessment of some default options that are used in carcinogen risk assessments. The research approach employed can be a useful strategy for developing mechanistic and toxicokinetic data to supplant default assumptions used in carcinogen risk assessments.

The National Research Council (NRC) recently published a report. Science and Judgment in Risk Assessment, that critiqued the current approaches to characterizing human cancer risks from exposure to chemicals. One issue raised in the report relates to the use of default options for quantitation of cancer risks. Default options are general guidelines that can be used for risk assessment when specific information about a chemical is absent. Research on 1,3-butadiene represents an interesting case study in which existing knowledge on this chemical indicates that two default options may no longer be tenable: (1) humans are as sensitive as the most sensitive animal species, and (2) the rate of metabolism is a function of body surface area rather than inherent species differences in metabolic capacity. Butadiene, a major commodity chemical used in the production of synthetic rubber, is listed as one of 189 hazardous air pollutants under the 1990 Clean Air Act Amendments. Butadiene is a carcinogen in rats and mice, with mice being substantially more sensitive than rats. The extent to which butadiene poses a cancer risk to humans exposed to this chemical is uncertain. Butadiene requires metabolic activation to DNA-reactive epoxides to exert its mutagenic and carcinogenic effects. Research is directed toward obtaining a better understanding of the cancer risks of butadiene in humans by evaluating species-dependent differences in the formation of the toxic butadiene epoxide metabolites, epoxybutene and diepoxybutane. The data include in-vitro studies on butadiene metabolism using tissues from humans, rats, and mice as well as experimental data and physiological model predictions for butadiene in blood and butadiene epoxides in blood, lung, and liver after exposure of rats and mice to inhaled butadiene. The findings suggest that humans are more like rats and less like mice regarding the formation of butadiene epoxides. The research approach employed can be a useful strategy for developing mechanistic and toxicokinetic data to supplant default options used in carcinogen risk assessments for butadiene.

1,3-Butadiene (BD) is carcinogenic in B6C3F1 mice and Sprague-Dawley rats, and mice are more sensitive than rats. This study measured the concentrations of the putative DNA-reactive BD metabolites, butadiene monoxide (BMO) and butadiene diepoxide (BDE), in lung and liver of male Sprague-Dawley rats and B6C3F1 mice exposed to BD by inhalation. Samples (n = 3-6) of lung and liver were collected at 3 and 6 hr during and at 6 and 12 min following 6-hr nose-only inhalation exposure to 0, 62.5, 625, 1250, or 8000 (rats only) ppm BD. BMO and BDE were extracted into methylene chloride and quantified by gas chromatography-mass spectrometry. Since BD epoxides can be conjugated with glutathione (GSH), the nonprotein sulfhydryl content of lung and liver was quantified colorimetrically. Analytical limitations precluded quantitation of BD epoxides in tissues of rats or mice exposed to 62.5 ppm BD. Exposures greater than or equal to 625 ppm BD resulted in higher BMO concentrations in lungs and livers of mice compared to rats. In mice exposed to 625 and 1250 ppm BD, the maximum concentrations of BMO at 3 or 6 hr of exposure in lungs (2.6 +/- 0.2 and 3.7 +/- 1.2 nmol/g tissue; mean +/- SE) were higher than in livers (0.58 +/- 0.12 and 0.93 +/- 0.19 nmol/g). Rats exposed to 625 and 1250 ppm BD had lower concentrations of BMO in lungs (0.16 +/- 0.03 and 0.31 +/- 0.07 nmol/g) and livers (0.06 +/- 0.01 and 0.16 +/- 0.06 nmol/g) than mice. In rats exposed to 8000 ppm BD, the maximum concentrations of BMO in lungs (1.3 +/- 0.2 nmol/g) and livers (1.2 +/- 0.1 nmol/g) were nearly identical. BDE was quantified in lungs, but not livers, of mice exposed to 625 and 1250 ppm BD. The maximum concentrations of BDE in mouse lungs were 0.71 +/- 0.06 and 1.5 +/- 0.1 nmol/g, respectively; BDE was not detected in livers or lungs of rats exposed to any of the concentrations of BD tested. GSH depletion was dependent on the concentration and duration of BD exposure. The lungs of mice sustained the greatest magnitude of depletion (26% of control at 6 hr of exposure to 1250 ppm BD).(ABSTRACT TRUNCATED AT 400 WORDS)

1,3-Butadiene (BD), an important commodity chemical used in the production of synthetic rubber, is carcinogenic in B6C3F1 mice and Sprague-Dawley rats, raising concern for potential carcinogenicity in humans. Mice are more sensitive than rats to the carcinogenic effects of BD. Metabolic activation of BD to form the putative DNA-reactive metabolites, butadiene monoxide (BMO) and butadiene diepoxide (BDE), is mediated by cytochrome P450. Detoxication of the epoxides occurs by glutathione S-transferase-catalyzed conjugation with glutathione and hydrolysis by epoxide hydrolase. Species differences in metabolic activation and detoxication most likely contribute to the difference in carcinogenic potency of BD by modulating the circulating blood levels of the epoxides. This study measured the in vivo concentrations of BD, BMO and BDE in the blood of male Sprague-Dawley rats and B6C3F1 mice during and following 6 h nose-only exposure to inhaled BD at 62.5, 625 or 1250 p.p.m. BD. Blood samples for BD and BMO (> or = 3 samples/time point) were collected at 2, 3, 4 and 6 h of exposure. Blood samples for BDE were collected at 3 and 6 h of exposure. After exposure, blood samples for BD, BMO and BDE were collected at 2-10 min intervals up to 30 min post-exposure. BD was quantified by gas chromatography using a vial headspace equilibration technique. BD epoxides were extracted into methylene chloride and quantified by gas chromatography-mass spectrometry. The concentration of BD in blood was not directly proportional to the inhaled concentration of BD, suggesting that the uptake of BD was saturable at the highest inhaled concentration. In both rats and mice, BD and BMO blood levels were at steady-state at 2, 3, 4 and 6 h of exposure, and declined rapidly after removal from exposure to BD. Steady-state blood concentrations of BD were 2.4, 37 and 58 microM in mice and 1.3, 18 and 37 microM in rats exposed to 62.5, 625 and 1250 p.p.m. BD respectively. Both species formed BMO from BD. In mice the respective steady-state BMO concentrations in blood were 0.6, 3.7 and 8.6 microM, compared to BMO blood concentrations in rats of 0.07, 0.94 and 1.3 microM. Mice, but not rats, had quantifiable levels of BDE in the blood. The peak concentrations of BDE in the blood of mice at 6 h were 0.65, 1.9 and 2.5 microM.(ABSTRACT TRUNCATED AT 400 WORDS)

A unified physiologically based pharmacokinetic (PB-PK) model was developed and used to describe the disposition of methylchloroform (1,1,1-trichloroethane, MC) in three different species (rats, mice, and humans) after four different routes of exposure (inhalation, intravenous injection, bolus gavage, and drinking water administration). Metabolism of MC followed Michaelis-Menten kinetics in each species. Vmax's were calculated from the allometric equation: Vmax = 0.419 BW0.7, and Km appeared to be identical in each species (5.75 mg equivalents/liter). Once the PB-PK model had been developed for young adult animals (1-3 months of age), it was used to study the disposition of MC in older rats and mice (approximately 18.5 months of age). Most of the changes in the pharmacokinetic behavior of MC in older rats could be simulated by increasing the size of the fat compartment in the PB-PK model from 7 to 18% of body weight. However, the pharmacokinetic behavior in older mice was more complex; increasing the size of the fat compartment in this species from 4 to 18% only accounted for part of the observed differences between old and young animals. An appropriate dose surrogate (average area under the liver concentration/time curve) was selected and the PB-PK model was used to make quantitative comparisons between "internal doses" of MC in long term animal studies and "internal doses" associated with human exposures to MC. Values of the dose surrogate in humans consuming 2 liters/day of water with typical levels of MC contamination (1-10 ppb) were four to six orders of magnitude lower than the dose surrogates in the rodent studies at levels of MC exposure which failed to produce adverse effects on the liver (875-1500 ppm, 6 hr/day, 5 days/week).