Mode of action assessment for propylene dichloride as a human carcinogen.

As part of a systematic review of the non-cancer and cancer hazards of propylene dichloride (PDC), with a focus on potential carcinogenicity in workers following inhalation exposures, we determined that a mode of action (MOA)-centric framing of cancer effects was warranted. In our MOA analysis, we systematically reviewed the available mechanistic evidence for PDC-induced carcinogenesis, and we mapped biologically plausible MOA pathways and key events (KEs), as guided by the International Programme on Chemical Safety (IPCS)-MOA framework. For the identified pathways and KEs, biological concordance, essentiality of KEs, concordance of empirical observations among KEs, consistency, and analogy were evaluated. The results of this analysis indicate that multiple biologically plausible pathways may contribute to the cancer MOA for PDC, but that the relevant pathways vary by exposure route and level, tissue type, and species; further, more than one pathway may occur concurrently at high exposure levels. While several important data gaps exist, evidence from in vitro mechanistic studies, in vivo experimental animal studies, and ex vivo human tumor tissue analyses indicates that the predominant MOA pathway likely involves saturation of cytochrome p450 2E1 (CYP2E1)-glutathione (GSH) detoxification (molecular initiating event; MIE), accumulation of CYP2E1-oxidative metabolites, cytotoxicity, chronic tissue damage and inflammation, and ultimately tumor formation. Tumors may occur through several subsets of inflammatory KEs, including inflammation-induced aberrant expression of activation-induced cytidine deaminase (AID), which causes DNA strand breaks and mutations and can lead to tumors with a characteristic mutational signature found in occupational cholangiocarcinoma. Dose concordance analysis showed that low-dose mutagenicity (from any pathway) is not a driving MOA, and that prevention of target tissue damage and inflammation (associated with saturation of CYP2E1-GSH detoxification) is expected to also prevent the cascade of processes responsible for tumor formation.

Derivation of cancer no significant risk levels and screening safety assessment for 2-nitropropane in spray products.

Two proposition 65 no-significant-risk level (NSRL)-type values were derived for 2-nitropropane (2-NP), in the absence of a Californian published NSRL. In addition, a safety assessment was performed based on estimated typical consumer inhalation and dermal exposure to 2-NP during indoor application of paint from a spray can containing the solvent 1-nitropropane. For the NSRL derivation, benchmark dose (BMD) modeling was performed using hepatocellular carcinoma incidence data from 2-NP single exposure inhalation studies in Sprague-Dawley rats. Several BMD models provided an acceptable fit for the male rat hepatocellular carcinoma incidence data (gamma, log-probit, log-logistic and multistage); therefore, the mean of the BMD lower limits from each model were used as the point of departure to derive the inhalation cancer potency. The oral human cancer potency was derived from the inhalation human cancer potency based on the ratio of the uptake factors for inhalation vs. oral routes. The derived inhalation and oral NSRLs are 67 µg/day and 32 µg/day, respectively. For the inhalation and dermal exposure assessment, three key factors were analyzed: the 2-NP residual concentration in the spray paint product, the mass of spray paint used and the frequency of use. Based on the screening exposure assessment, potential consumer inhalation and dermal exposure to 2-NP from indoor application of paint from a spray can does not exceed our proposed NSRLs, and a warning label is therefore not required for spray can products containing the solvent 1-nitropropane where 2-NP is a minor contaminant.

RIFM fragrance ingredient safety assessment, 1-(1,2,3,4-tetrahydro-4,4-dimethyl-1-naphthyl)propan-1-one, CAS Registry Number 74499-60-8.

The use of this material under current use conditions is supported by the existing information. This material was evaluated for genotoxicity, repeated dose toxicity, developmental and reproductive toxicity, local respiratory toxicity, phototoxicity/photoallergenicity, skin sensitization, as well as environmental safety. Data from the target material and the suitable read across analog 6-acetyl-1,1,2,4,4,7-hexamethyltetraline (CAS # 21145-77-7) show that this material is not genotoxic. Data from the suitable read across analog 6-acetyl-1,1,2,4,4,7-hexamethyltetraline (CAS # 21145-77-7) provided a MOE > 100 for the repeat dose and developmental toxicity endpoints. The reproductive and local respiratory toxicity endpoints were completed using the TTC (Threshold of Toxicological Concern) for a Cramer Class II material (0.009 mg/kg/day and 0.47 mg/day, respectively). Data on the target material showed that this material is below the non-reactive DST for skin sensitization and did not have the potential for phototoxicity or photoallergenicity. The environmental endpoint was completed as described in the RIFM Framework.

Assessment of the genotoxicity of 1,2-dichloropropane and dichloromethane after individual and co-exposure by inhalation in mice.

OBJECTIVE: Occurrence of cholangiocarcinoma was recently reported at a high incidence rate among the employees working for an offset printing company in Osaka, Japan. 1,2-Dichloropropane (1,2-DCP) and dichloromethane (DCM) are suspected to be the causes of the cancer, as they had been used as ink cleaners in large amounts. However, it is not clear whether these chlorinated organic solvents played a role in the occurrence of cholangiocarcinoma or why the incidence rate is so high among the workers in this industry. To provide possible evidence for this severe occupational problem, we investigated the genotoxic effects of 1,2-DCP and DCM. METHODS: Male B6C3F1 and gpt Delta C57BL/6J mice were exposed by inhalation to the individual solvents or both solvents at multiple concentrations including the levels that were possibly present in the workplaces. The genotoxicity was analyzed by Pig-a gene mutation and micronuclei assays in peripheral blood and gpt mutation and comet assays in the livers of mice after repeated inhalation of 1,2-DCP or/and DCM. RESULTS: The Pig-a mutant frequencies and micronuclei incidences were not significantly increased by exposure of either 1,2-DCP or/and DCM at any concentration, suggesting there was no genotoxic potential in bone marrow for both solvents. In the liver, DNA damage, as measured by the comet assay, was dose dependently increased by 1,2-DCP but not by DCM. The gpt mutant frequency was 2.6-fold that of the controls in the co-exposure group. CONCLUSIONS: These results indicate that 1,2-DCP showed stronger genotoxicity in the liver and that the genotoxic effects were greatly enhanced by simultaneous exposure to DCM.

Assessment of inhibin B as a biomarker of testicular injury following administration of carbendazim, cetrorelix, or 1,2-dibromo-3-chloropropane in Wistar han rats.

Although histopathology is considered the gold standard for assessing testicular toxicity in the nonclinical setting, identification of noninvasive biomarkers for testicular injury are desirable to improve safety monitoring capabilities for clinical trials. Inhibin B has been investigated as a noninvasive biomarker for testicular toxicity. This study investigates the correlation of Inhibin B in Wistar Han rats with the onset and reversibility of testicular histopathology from classical testicular toxicants carbendazim, cetrorelix acetate (CTX), and 1,2-dibromo-3-chloropropane (DBCP). The dose regimen included Interim (day 8), Drug (day 29), and nondosing Recovery (day 58) Phases. Inhibin B was not effective at predicting the onset of carbendazim- or CTX-mediated testicular pathology in rats. Inhibin B was reduced by DBCP administration at the end of the Drug Phase only, acting as a leading indicator of the onset of testicular toxicity before the onset of germ cell depletion. However, since Inhibin B was only decreased at the end of the Dosing Phase and not at the Recovery Phase, when the onset of testicular pathology occurred, it is unclear if monitoring Inhibin B would provide sufficient advanced warning for the onset of testicular pathology. Furthermore, follicle stimulating hormone was decreased following CTX and DBCP administration in the Interim Phase and CTX in the Drug Phase. Inhibin B has limited predictive capacity as a leading testicular biomarker in rats.

Approaches to cancer assessment in EPA's Integrated Risk Information System.

The U.S. Environmental Protection Agency's (EPA) Integrated Risk Information System (IRIS) Program develops assessments of health effects that may result from chronic exposure to chemicals in the environment. The IRIS database contains more than 540 assessments. When supported by available data, IRIS assessments provide quantitative analyses of carcinogenic effects. Since publication of EPA's 2005 Guidelines for Carcinogen Risk Assessment, IRIS cancer assessments have implemented new approaches recommended in these guidelines and expanded the use of complex scientific methods to perform quantitative dose-response assessments. Two case studies of the application of the mode of action framework from the 2005 Cancer Guidelines are presented in this paper. The first is a case study of 1,2,3-trichloropropane, as an example of a chemical with a mutagenic mode of carcinogenic action thus warranting the application of age-dependent adjustment factors for early-life exposure; the second is a case study of ethylene glycol monobutyl ether, as an example of a chemical with a carcinogenic action consistent with a nonlinear extrapolation approach. The use of physiologically based pharmacokinetic (PBPK) modeling to quantify interindividual variability and account for human parameter uncertainty as part of a quantitative cancer assessment is illustrated using a case study involving probabilistic PBPK modeling for dichloromethane. We also discuss statistical issues in assessing trends and model fit for tumor dose-response data, analysis of the combined risk from multiple types of tumors, and application of life-table methods for using human data to derive cancer risk estimates. These issues reflect the complexity and challenges faced in assessing the carcinogenic risks from exposure to environmental chemicals, and provide a view of the current trends in IRIS carcinogenicity risk assessment.

Derivation of a reference dose and drinking water equivalent level for 1,2,3-trichloropropane.

In some US potable water supplies, 1,2,3-trichloropropane (TCP) has been present at ranges of non-detect to less than 100 ppb, resulting from past uses. In subchronic oral studies, TCP produced toxicity in kidneys, liver, and other tissues. TCP administered by corn oil gavage in chronic studies produced tumors at multiple sites in rats and mice; however, interpretation of these studies was impeded by substantial premature mortality. Drinking water equivalent levels (DWELs) were estimated for a lifetime of consumption by applying biologically-based safety/risk assessment approaches, including Monte Carlo techniques, and with consideration of kinetics and modes of action, to possibly replace default assumptions. Internationally recognized Frameworks for human relevance of animal data were employed to interpret the findings. Calculated were a reference dose (=39 microg/kg d) for non-cancer and Cancer Values (CV) (=10-14 microg/kg d) based on non-linear dose-response relationships for mutagenicity as a precursor of cancer. Lifetime Average Daily Intakes (LADI) are 3130 and 790-1120 microg/person-d for non-cancer and cancer, respectively. DWELs, estimated by applying a relative source contribution (RSC) of 50% to the LADIs, are 780 and 200-280 microg/L for non-cancer and cancer, respectively. These DWELs may inform establishment of formal/informal guidelines and standards to protect public health.

Assessment in rats of the gonadotoxic and hepatorenal toxic potential of dibromochloropropane (DBCP) in drinking water.

This investigation was undertaken to assess the potential of ingested 1,2-dibromo-3-chloropropane (DBCP) to cause testicular and hepatorenal injury, in light of the paucity of data applicable to risk assessment of DBCP in drinking water. Adult male Sprague-Dawley rats were supplied ad libitum with water containing 0, 5, 50, 100, and 200 ppm DBCP for 64 days. A dose-related decrease in water consumption occurred during the study. The 200-ppm animals drank less than half as much water as controls, consumed less food, and subsequently exhibited significantly lower body weight gain. DBCP ingestion thus was not directly proportional to the level of chemical in the water, although daily and cumulative intake of DCP were concentration dependent. Average daily intake of DBCP for the 64-day exposure period was as follows: 5 ppm = 0.4 mg/kg/day; 50 ppm = 3.3 mg/kg/day; 100 ppm = 5.4 mg/kg/day; 200 ppm = 9.7 mg/kg/day. Blood samples were taken after 2, 4, and 6 weeks of exposure and at the terminal sacrifice and assayed for serum glutamic-oxaloacetic transaminase, glutamic-pyruvic transaminase, sorbitol dehydrogenase, and ornithine-carbamyl transferase activities and BUN levels. No evidence of liver damage at any exposure level was indicated by either the clinical chemistry indices or histopathology. Histologic examination revealed an apparent increase in the number of nuclei per renal proximal tubule cross-section in the 200-ppm group, possibly indicative of an increased turnover of proximal tubular cells. A slight, but statistically significant, decrease in absolute testicular weight was manifest in the 200-ppm animals, although the decrease was not significant when testicular weight was calculated as g/100 g body wt. Epididymal sperm counts and serum luteinizing hormone, follicle stimulating hormone, and intratesticular testosterone levels were not altered by any dose of DBCP. A qualitative histopathological examination of the testicular seminiferous epithelium failed to reveal any abnormalities in the spermatogenic process.

Integrating uncertainty and interindividual variability in environmental risk assessment.

An integrated, quantitative approach to incorporating both uncertainty and interindividual variability into risk prediction models is described. Individual risk R is treated as a variable distributed in both an uncertainty dimension and a variability dimension, whereas population risk I (the number of additional cases caused by R) is purely uncertain. I is shown to follow a compound Poisson-binomial distribution, which in low-level risk contexts can often be approximated well by a corresponding compound Poisson distribution. The proposed analytic framework is illustrated with an application to cancer risk assessment for a California population exposed to 1,2-dibromo-3-chloropropane from ground water.

Assessment of procedures for screening agents for effects on male reproduction: effects of dibromochloropropane (DBCP) on the rat.

This study was designed to evaluate new protocols proposed for use as an initial screen or a dose-response test of an agent for adverse effects on male reproduction. Seven groups of adult male rats (15/group) were nongavaged or received orally 0.00, 0.94, 1.88, 3.75, 7.5, or 15.0 mg/kg of 1,2-dibromo-3-chloropropane (DBCP) in corn oil each day for 77 days. From Day 65 to Day 71, each male was caged with 2 untreated female rats. Pregnancy rate and the ratio between the numbers of embryos and corpora lutea were determined. Males were killed on Day 78 and blood was collected and one testis and epididymis were used to determine daily spermatozoal production and epididymal spermatozoal reserves. The contralateral testis was fixed for quantitative histologic evaluation. Considering only data for the 15.0 and 0.00 mg/kg doses, as in an initial screen, DBCP would have been identified as a compound of concern. Body weight, paired testicular weight, parenchymal weight of the left testis, daily spermatozoal production per testis, numbers of sperm in the caput-corpus or cauda epididymidis, mean diameter of seminiferous tubules, and the ratio of leptotene spermatocytes to Sertoli cells were reduced (p less than 0.05). Fertility was normal, but the incidence of dead embryos and the ratio of dead embryos to corpora lutea were increased. Considering all data, as in a dose-response test, discriminant analysis was more sensitive in distinguishing treated rats from those receiving 0.0 mg DBCP/kg than was univariate analysis of variance. Using DBCP as a test compound, it was concluded that use of relatively simple, objective criteria in a test lasting approximately 10 weeks will be useful in identifying agents requiring detailed scrutiny.