Differing hepatotoxicity and lethality after subacute trichloroethylene exposure in aqueous or corn oil gavage vehicles in B6C3F1 mice

Final Report of the Safety Assessment of Cosmetic Ingredients Derived From Zea Mays (Corn)

Many cosmetic ingredients are derived from Zea mays (corn). While safety test data were not available for most ingredients, similarities in preparation and the resulting similar composition allowed extrapolation of safety data to all listed ingredients. Animal studies included acute toxicity, ocular and dermal irritation studies, and dermal sensitization studies. Clinical studies included dermal irritation and sensitization. Case reports were available for the starch as used as a donning agent in medical gloves. Studies of many other endpoints, including reproductive and developmental toxicity, use corn oil as a vehicle control with no reported adverse effects at levels used in cosmetics. While industry should continue limiting ingredient impurities such as pesticide residues before blending into a cosmetic formulation, the CIR Expert Panel determined that corn-derived ingredients are safe for use in cosmetics in the practices of use and concentration described in the assessment.

Applying Mode-of-Action and Pharmacokinetic Considerations in Contemporary Cancer Risk Assessments: An Example with Trichloroethylene

The guidelines for carcinogen risk assessment recently proposed by the U.S. Environmental Protection Agency (U.S. EPA) provide an increased opportunity for the consideration of pharmacokinetic and mechanistic data in the risk assessment process. However, the greater flexibility of the new guidelines can also make their actual implementation for a particular chemical highly problematic. To illuminate the process of performing a cancer risk assessment under the new guidelines, the rationale for a state-of-the-science risk assessment for trichloroethylene (TCE) is presented. For TCE, there is evidence of increased cell proliferation due to receptor interaction or cytotoxicity in every instance in which tumors are observed, and most tumors represent an increase in the incidence of a commonly observed, species-specific lesion. A physiologically based pharmacokinetic (PBPK) model was applied to estimate target tissue doses for the three principal animal tumors associated with TCE exposure: liver, lung, and kidney. The lowest points of departure (lower bound estimates of the exposure associated with 10% tumor incidence) for lifetime human exposure to TCE were obtained for mouse liver tumors, assuming a mode of action primarily involving the mitogenicity of the metabolite trichloroacetic acid (TCA). The associated linear unit risk estimates for mouse liver tumors are 1.5 x 10(-6) for lifetime exposure to 1 microg TCE per cubic meter in air and 0.4 x 10(-6) for lifetime exposure to 1 microg TCE per liter in drinking water. However, these risk estimates ignore the evidence that the human is likely to be much less responsive than the mouse to the carcinogenic effects of TCA in the liver and that the carcinogenic effects of TCE are unlikely to occur at low environmental exposures. Based on consideration of the most plausible carcinogenic modes of action of TCE, a margin-of-exposure (MOE) approach would appear to be more appropriate. Applying an MOE of 1000, environmental exposures below 66 microg TCE per cubic meter in air and 265 microg TCE per liter in drinking water are considered unlikely to present a carcinogenic hazard to human health.

Comparison of available benchmark dose softwares and models using trichloroethylene as a model substance

By using trichloroethylene as a model substance the U.S. EPA benchmark dose software was compared to the software by Crump and the software by Kalliomaa. Dose-response and dose-effect data on the liver, kidneys, central nervous system (CNS), and tumours were selected for the evaluation. Based on the present study the U.S. EPA software is preferable to the other softwares for dichotomous data. A wider range in benchmark doses was often observed for dichotomous data when the numbers of dose levels were limited. The log-logistic model in most cases gave the best fit when ranking the dichotomous models. In addition, the log-logistic model often implied a more conservative benchmark dose. For continuous data it was more difficult to find a model describing the data. The softwares by Kalliomaa and by the U.S. EPA offered the best opportunities for benchmark dose modelling of continuous data. Flexible models, like the Hill- and the Mult model, are needed for S-shaped continuous data but these models demand more dose levels in order to describe the data. Since the number of dose levels are important for model selection study design is important and should be further evaluated.

Toxicosis associated with dual oral exposure of rats to lead and trichloroethylene

To determine if additive or synergistic toxic effects would occur, adult male rats were exposed orally to lead carbonate (2,000 mg/kg) for 9 days before trichloroethylene (TCE), 2,000 mg/kg, was given concurrently for an additional 7 days. Comparisons were made with groups of vehicle-treated rats and rats given only lead or only TCE. Potential neurotoxicity was evaluated by using the Functional Observational Battery (FOB) recommended for neurotoxicity screening. Rats were sacrificed on day 16, and brain, testes, spleen, kidney/adrenals, heart, and liver weighed and observed for pathological changes. Results of the FOB indicated that lead carbonate was more responsible than TCE for changes observed. Additive or synergistic neurotoxicities were not noted. Histological examination of the kidney from lead-treated rats revealed inclusions, an increased incidence of coagulated proteins, and tubular dilation that was generally more severe in the medullary segments. Gastric and testicular necrosis were found in rats given lead carbonate both with and without TCE (15/20 and 6/20 treated, respectively). The results suggest that, even when given concurrently, the toxicities of lead carbonate and TCE are expressed only as though one toxicant was given.

Chloroform mode of action: implications for cancer risk assessment

Risk assessment methodology, particularly pertaining to potential human carcinogenic risks from exposures to environmental chemicals, is undergoing intense scrutiny from scientists, regulators, and legislators. The current practice of estimating human cancer risk is based almost exclusively on extrapolating the results of chronic, high-dose studies in rodents to estimate potential risk in humans. However, many scientists are questioning whether the logic used in this current risk assessment methodology is the best way to safeguard public health. A major tool of human cancer risk assessment is the linearized multistage (LMS) model. The LMS model has been identified as an aspect of risk assessment that could be improved. One way to facilitate this improvement is by developing a way to incorporate a carefully derived, more biologically relevant mechanism of action data on carcinogenesis. Recent data on chloroform indicate that the dose-response relationship for chloroform-induced tumors in rats and mice is nonlinear, based upon events secondary to cell necrosis and subsequent regeneration as the likely mode of action for the carcinogenic effects of chloroform. In light of these data, there is a sound scientific basis for removing some of the uncertainty that accompanies current cancer risk assessments of chloroform. The following points summarize the critical data: (1) a substantial body of data demonstrates a lack of direct in vivo or in vitro genotoxicity of chloroform; (2) chloroform induces liver and kidney tumors in long-term rodent cancer bioassays only at doses that induce frank toxicity at these target sites; (3) the chloroform doses required to produce tumors in susceptible species exceed the MTD, often by a considerable margin; (4) cytotoxicity and compensatory cell proliferation are associated with the chloroform doses required to induce liver or kidney tumors in susceptible rodent species; (5) there are no instances of chloroform-induced tumors that are not preceded by this pattern of dose-dependent toxic responses; (6) it is biologically plausible that cytolethality leads to chronically stimulated cell proliferation and related events such as inflammation and growth stimulation which act to initiate and promote the carcinogenic process; and (7) the consistently linked cellular events of cytolethality and subsequent cell proliferation, for which doses of no adverse effect have been clearly shown to exist, are one of the biological prerequisites for chloroform-induced tumors in animals. Based on these data, it is inappropriate to extrapolate cancer risk from high doses that produce necrosis and regenerative cell proliferation to low doses that do not with a model that presumes genotoxicity and a linear dose-response relationship. The weight of the scientific evidence concerning chloroform-induced tumors in rodents is consistent with and supports a cancer risk assessment methodology based on mode of action as the basis for establishing regulatory standards for this compound.

Effect of dosing vehicle on the hepatotoxicity of CCl4 and nephrotoxicity of CHCl3 in rats

There are conflicting results in the literature concerning the effect of gavage vehicle, corn oil (CO) versus aqueous suspension, on the toxicity of haloalkanes. The purpose of our study was to assess the influence of oral dosing vehicle on the acute hepatotoxicity of CCl4 and nephrotoxicity of CHCl3. Male Sprague-Dawley rats, fed ad libitum, were treated (po) with single doses of CCl4 or CHCl3 using corn oil (CO), or an aqueous preparation (5%) of Emulphor (EL620) or Tween-85 (Tw-85) as vehicle (10 ml/kg). Rats were killed 48 h after treatment. Blood was collected for plasma alanine aminotransferase (ALT) determination and renal cortical slices were prepared for p-aminohippuric acid (PAH) incorporation. The comparison, between gavage vehicles, of the slopes and ED50 of the dose-response curves, although not significantly different, indicated clear trends for enhanced potency with CO for CHCl3 nephrotoxicity but not for CCl4 hepatotoxicity. However, ALT values, a measure of the severity of effect for CCl4, also indicated that CO, when compared to EL620 and Tw-85, tended to enhance CCl4 hepatotoxicity at low toxicity incidence. Furthermore, CO clearly enhanced the severity of effect for CHCl3 nephrotoxicity, as measured by the slice-to-medium PAH ratios, at high dosage. The greater severity of the lesion produced by exposure to these chemicals, when administered in CO, is consistent with the trends observed for their potency (dose-response curves). Our results agree with an increased toxicity of haloalkanes by the gavage vehicle CO reported in the literature. Thus, CO should be considered a potential confounder in hepato- and nephrotoxicity assays.

Effect of subchronic corn oil gavage on the acute toxicity of orally administered bromodichloromethane

Bromodichloromethane (BDCM) is a by-product of water chlorination and is the second most common trihalomethane (THM) in finished drinking water. It has been reported that delivery of THMs in corn oil can influence the site and magnitude of toxic and carcinogenic responses in rodents, perhaps by inducing metabolizing enzymes or altering tissue composition. To determine if corn oil influences the acute toxicity of BDCM, adult male F-344 rats were pretreated 5 days/week for 6 weeks with oral doses of corn oil or water at a volume of 5 ml/kg. Following pretreatment, animals were gavaged with a single dose of 0, 200 or 400 mg BDCM/kg in 10% Emulphor. Urine was collected at timed intervals over a 48-h period following BDCM administration. Rats were sacrificed at this time and organs and blood removed. Urine and serum were analyzed for indicators of toxicity. Corn oil pretreatment did not enhance the acute hepato- or nephrotoxicity of BDCM, suggesting that vehicle effects noted in previous THM toxicity and carcinogenicity studies are more likely due to pharmacokinetic differences between administration in corn oil and aqueous gavage vehicles than to altered tissue composition or physiological changes.

Evaluating human variability in chemical risk assessment: hazard identification and dose-response assessment for noncancer oral toxicity of trichloroethylene

Human variability can be addressed during each stage in the risk assessment of chemicals causing noncancer toxicities. Noncancer toxicities arising from oral exposure to trichloroethylene (TCE) are used in this paper as a case study for exploring strategies for identifying and incorporating information about human variability in the chemical specific hazard identification and dose-response assessment steps. Toxicity testing in laboratory rodents is the most commonly used method for hazard identification. By using animal models for sensitive populations, such as developing fetuses, testing can identify some potentially sensitive populations. A large variety of reproductive and developmental studies with TCE were reviewed. The results were mostly negative and the limited positive findings generally occurred at doses similar to those causing liver and kidney toxicity. Physiologically based pharmacokinetic modeling using Monte Carlo simulation is one method for evaluating human variability in the dose-response assessment. Three strategies for obtaining data describing this variability for TCE are discussed: (1) using in vivo human pharmacokinetic data for TCE and its metabolites, (2) studying metabolism in vitro, and (3) identifying the responsible enzymes and their variability. A review of important steps in the metabolic pathways for TCE describes known metabolic variabilities including genetic polymorphisms, enzyme induction, and disease states. A significant problem for incorporating data on pharmacokinetic variability is a lack of information on how it relates to alterations in toxicity. Response modeling is still largely limited to empirical methods due to the lack of knowledge about toxicodynamic processes. Empirical methods, such as reduction of the No-Observed-Adverse-Effect-Level or a Benchmark Dose by uncertainty factors, incorporate human variability only qualitatively by use of an uncertainty factor. As improved data and methods for biologically based dose-response assessment become available, use of quantitative information about variability will increase in the risk assessment of chemicals.

Effect of oral dosing vehicles on the subchronic hepatotoxicity of carbon tetrachloride in the rat

Previous studies in this laboratory have shown that corn oil delayed and prolonged the gastrointestinal absorption of carbon tetrachloride (CCl4) and reduced its acute hepatotoxicity in rats. The objective of the present study was to extend the duration of ingestion of CCl4 to assess vehicle effects on the subchronic oral toxicity of CCl4. Male Harlan Sprague-Dawley rats were given doses of 0, 25, or 100 mg CCl4/kg body weight by gavage in either corn oil or a 1% Emulphor aqueous emulsion 5 times a week for 13 wk. Blood was collected at 4, 8, and 13 wk for measurement of serum enzymes. Liver samples were also taken at 13 wk for measurement of triglyceride and microsomal enzyme levels, as well as for histopathological examination. Serum enzyme levels peaked at 8 wk in the high-dose groups, but not until 13 wk in the low-dose animals. Effects of CCl4 on serum and microsomal enzymes were of similar magnitude in the two vehicle groups. A comprehensive histopathological examination revealed no qualitative or quantitative differences between the corn oil and aqueous vehicle groups in hepatic lesions. Although CCl4 and chloroform have been reported by other investigators to be more hepatotoxic to mice when given for 90 d in corn oil, current findings indicate that corn oil does not significantly alter the subchronic hepatotoxicity of CCl4 in rats from that when the halocarbon is given in an aqueous medium.

A physiological and system analysis hybrid pharmacokinetic model to characterize carbon tetrachloride blood concentrations following administration in different oral vehicles

Oral absorption of chemicals can be influenced significantly by the administration vehicle or diluent. It has been observed that the oral absorption of carbon tetrachloride (CCl4) and other volatile organic chemicals is markedly affected by the dosing vehicle, with administration in oils producing erratic blood concentration-time profiles with multiple peaks. Analysis of this type of data by a compartmental modeling approach can be difficult, and requires numerous assumptions about the absorption processes. Alternatively, a system analysis method with few assumptions may provide a more accurate description of the observed data. In the current investigations, a nonlinear system analysis approach was applied to blood CCl4 concentration-time data obtained following iv and oral administration. The oral regimens consisted of 25 mg CCl4/kg body wt given as an aqueous emulsion, in water, as pure chemicals, and in corn oil. The system analysis procedure, based upon a disposition decomposition method, provided an absorption input rate function, F, for each regimen. A physiological pharmacokinetic model, based primarily on parameters available in the literature, and the F input functions, formed a hybrid model that adequately described the observed blood CCl4 concentration-time data. The same physiological pharmacokinetic model, employing conventional first-order absorption input schemes, did not predict the data as well. Overall, the system analysis approach allowed the oral absorption of CCl4 to be characterized accurately, regardless of the vehicle. Though system analysis is based on general mathematical properties of a system's behavior rather than on its causal mechanisms, this work demonstrates that it can be a useful adjunct to physiological pharmacokinetic models.

Hepatotoxic interactions of ethanol with allyl alcohol or carbon tetrachloride in rats

To assess whether potential toxic interactions occur between ethanol and allyl alcohol or carbon tetrachloride following subacute, concurrent chemical exposure, male Fischer 344 rats, approximately 70 d of age, were given ethanol at 0, 0.05, 0.1, 0.2, or 0.5 ml/kg in corn oil daily by gavage for 14 d (ETOH group), or the same levels of ethanol with 21 mg allyl alcohol/kg (ALAC group), or the same levels of ethanol with 20 mg carbon tetrachloride/kg (CCL4 group). Hepatic response was assessed 24 h after the last dose. Interactions were evaluated by comparing the ETOH group with either the ALAC group or the CCL4 group using multivariate analysis of variance procedures. No statistically significant interaction was seen between the ETOH group and the ALAC group at the dosages used. Although an interaction between ethanol and carbon tetrachloride given simultaneously was not statistically significant, a small interactive effect on weight gain from d 0 to termination was apparent (p = .057). Exposure to ethanol alone resulted in a concentration-dependent decrease in absolute and relative liver weight, with a threshold between 0.05 and 0.1 ml/kg. There was no histopathological evidence of hepatic damage with ethanol alone, and no effect on hepatic cytochrome P-450 and glutathione levels or on serum levels of alanine aminotransferase (ALT), aspartate aminotransferase (AST), and alkaline phosphatase (ALK). Exposure to allyl alcohol alone resulted in significant increases in absolute and relative liver weights, liver glutathione, and periportal hepatocellular vacuolar degeneration. Exposure to carbon tetrachloride alone resulted in significant increases in absolute and relative liver weight, serum levels of ALT, AST, and ALK, and centrilobular hepatocellular vacuolar degeneration and necrosis. These observations indicate that subacute, concurrent exposure of ethanol with carbon tetrachloride or allyl alcohol at ethanol levels comparable to those reported in gavage vehicles did not result in interactive toxicity.

Cardiopathic effect of 1,2,3-trichloropropane after subacute and subchronic exposure in rats

1,2,3-Trichloropropane (1,2,3-TCP) is an industrial water contaminant with potential for human exposure by the oral route. The systemic toxicology of 1,2,3-TCP was evaluated after subacute or subchronic exposure in male and female Sprague-Dawley rats. Animals were treated with 0.01, 0.05, 0.20 and 0.80 mmol kg-1 day-1 for 10 days and 0.01, 0.05, 0.10 and 0.40 mmol kg-1 day-1 for 90 days. Chemical exposure was by oral gavage in corn oil. Lethality did not occur in either study. Toxicity was observed primarily in the high dose group of subacute and subchronically treated rats of both sexes. Weight gain suppression occurred at a dose of 0.8 mmol kg-1 (118 mg kg-1) after 10 days. After 90 days of exposure to 0.40 mmol kg-1, the final body weights were 81% and 86% of control values for males and females, respectively. When major organ weights were normalized by body weight, liver and kidney values were generally increased relative to control in the two highest dose groups after 10- and 90-day chemical exposure. Serum chemistries and histopathology indicated a mild hepatotoxic response to 1,2,3-TCP in the high dose group of each study but did not support any renal toxicity. Thymic weight reduction due to atrophy occurred at 10 days of exposure in high dose groups but was normal in all groups after the 90-day treatment. The primary histological finding in this study was an inflammation-associated cardiopathy produced by 1,2,3-TCP. Myocardial necrosis and degeneration occurred in a diffuse pattern with marked eosinophilia of affected cells. Male and female animals showed a cardiopathic response only at a dose of 0.8 mmol kg-1 1,2,3-TCP after the 10-day exposure.(ABSTRACT TRUNCATED AT 250 WORDS)