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PubMed1993

A compartmental model for the prediction of breath concentration and absorbed dose of chloroform after exposure while showering.

In order to predict the exhaled breath concentration of chloroform in individuals exposed to chloroform while showering, an existing physiologically based pharmacokinetic (PB-PK) model was modified to include a multicompartment, PB-PK model for the skin and a completely mixed shower exposure model. The PB-PK model of the skin included the stratum corneum as the principal resistance to absorption and a viable epidermis which is in dynamic equilibrium with the skin microcirculation. This model was calibrated with measured exhaled breath concentrations of chloroform in individuals exposed while showering with and without dermal absorption. The calibration effort indicated that the expected value of skin-blood partitioning coefficient would be 1.2 when the degree of transfer of chloroform from shower water into shower air was 61%. The stratum corneum permeability coefficient for chloroform was estimated to be within the range of 0.16-0.36 cm/hr and the expected value was 0.2 cm/hr. The estimated ratio of the dermally and inhaled absorbed doses ranged between 0.6 and 2.2 and the expected value was 0.75. These results indicate that for the purposes of risk assessment for dermal exposure to chloroform, a simple steady-state model can be used to predict the degree of dermal absorption and that a reasonable value of skin permeability coefficient for chloroform used in this model would be 0.2 cm/hr. Further research should be conducted to compare the elimination of chloroform via exhaled breath when different exposure routes are being compared. The model results from this study suggest that multiple measurements of exhaled breath concentrations after exposure may be necessary when making comparisons of breath concentrations that involve different exposure routes.

Baths↗

PubMed1986

Lipid peroxidation in vivo monitored as ethane exhalation and malondialdehyde excretion in urine after oral administration of chloroform.

In vivo lipid peroxidation was studied in phenobarbital pretreated rats exposed for chloroform. Lipid peroxidation was monitored as ethane exhalation or malondialdehyde (MDA) excretion in urine. A single oral dose of chloroform (0.7 ml/kg b.wt.) showed a marked increase in ethane exhalation in animals starved for 48 hours prior to chloroform treatment. This increase became evident after a lag-period of about 100 min. Pretreatment with diethylmaleate (1 ml/kg b.wt.) 1 hour prior to chloroform treatment gave a similar result. MDA excretion in urine from non-starved animals, exposed to chloroform, markedly increased after 4 hours and after 24 hours 115 nmol/kg had been excreted. In animals starved for 48 hours prior to chloroform treatment about 270 nmol/kg excreted within 24 hours. Small molecular weight thiols were measured in liver, kidneys and lungs. Chloroform decreased the thiol content of the liver by 43.2% within 100 min. while the concentration in the kidneys and the lungs were less affected. It is suggested that chloroform may act as a potent inducer of lipid peroxidation in vivo. The synergistic effects of the pretreatments and the lag phase indicate that glutathione depletion in the liver was an essential factor in this response.

Administration, Oral↗

PubMed1992

Exposure of dental personnel to chloroform in root-filling procedures.

The exposure of dental personnel to chloroform in root-filling procedures was evaluated. Four different root filling procedures were studied. In all the procedures studied, guttapercha was used as the root-filling material and chloroform or sealers containing chloroform were used. Ten teeth in each group were root-filled. In the first group, chloroform and 5% rosin in chloroform were administered in medical cups, in the second group chloroform and Kloroperka NO was administered in medical cups. In Group three a specially designed glass tube (S-endodip) was used for administration and in the fourth group specially selected plastic tubes were used. In the last two groups the sealers were chloroform and 5% rosin in chloroform. When medical cups were used the exposure reached levels close to the accepted limit values in Sweden, indicating that only one root filling per day can be performed without the dental team being unacceptably exposed. Using either the glass tube or the specially designed plastic tube, the exposure was significantly reduced for the dentist (p < 0.005) and for the nurse (p < 0.005). The mean exposure was 19.1 mg/m3 for the dentist and 11.6 mg/m3 for the nurse in the first experimental group. The mean values in the second group were 15.4 mg/m3 and 16.6 mg/m3 respectively. In the third group, the dentist was exposed to a mean of 4.4 mg/m3 and the nurse to 6.3 mg/m3. In the fourth group, the mean exposure was 2.2 mg/m3 and 3.4 mg/m3 respectively.(ABSTRACT TRUNCATED AT 250 WORDS)

Chloroform↗

PubMed1983

Inactivation of hepatitis B virus and non-A, non-B hepatitis by chloroform.

To determine whether a non-A, non-B hepatitis agent contained essential lipids, we extracted with chloroform a dilution of human plasma that contained approximately 10(4) chimpanzee infectious doses of non-A, non-B hepatitis virus and then tested for infectivity in chimpanzees. In addition, we treated a serum containing hepatitis B virus in the same way. Both of these samples were also sham extracted as controls. Known chloroform-sensitive and chloroform-resistant viruses were added directly to the hepatitis-containing serum or plasma as internal controls or to fetal calf serum as external controls and were assayed for infectivity in vitro after chloroform extraction or sham extraction. All infectivity of the diluted plasma that contained at least 10(4) chimpanzee infective doses of non-A, non-B hepatitis agent and all infectivity of the serum that contained 10(3.5) chimpanzee infective doses of hepatitis B virus were destroyed by chloroform. The chloroform-sensitive control viruses were completely inactivated, but the chloroform-resistant control viruses lost less than 0.5 log10 of infectivity. Sham-extracted non-A, non-B hepatitis agent-containing plasma was shown to maintain its infectivity in chimpanzees that had initially been inoculated with the chloroform-extracted plasma. Thus, both hepatitis type B and non-A, non-B hepatitis appear to be caused by viruses that can be inactivated by a lipid solvent.

Animals↗

PubMed2003

The relationship between water concentrations and individual uptake of chloroform: a simulation study.

We simulated the relationship between water chloroform concentrations and chloroform uptake in pregnant women to assess the potential extent of exposure measurement error in epidemiologic studies of the health effects of exposure to water disinfection by-products. Data from the literature were used to assign statistical distributions to swimming pool chloroform concentrations, frequency and duration of swimming, showering and bathing, and average tap water consumption. Measured increases in blood chloroform concentrations after these activities were used to estimate average uptake per microgram per liter chloroform in the water, per minute spent in the activity or per liter consumed. Given average tap water chloroform concentrations from a U.K. epidemiologic study, an average daily uptake over 90 days was simulated for 300,000 mothers. The correlation between simulated uptakes and home tap chloroform concentration was 0.6. Mothers who swam regularly received far greater doses than did nonswimmers. Results suggest there will be considerable attenuation in risk estimates and/or power loss in epidemiologic studies if the putative agent is chloroform.

Adult↗

PubMed2004

The effects of in utero and lactational exposure to chloroform on postnatal growth and glucose tolerance in male Wistar rats.

Water chlorination results in the formation of trihalomethanes (THMs) including chloroform. In human stud-ies, fetal growth restriction has been associated with exposure to THMs during pregnancy and impaired fetal growth has been associated with an increased risk of type 2 diabetes. Therefore, the objective of this study was to determine the effect of in utero and lactational exposure to chloroform on birthweight and postnatal indicators of type 2 diabetes. Female Wistar rats were given chloroform (0 microg/L, 75 microg/L) in their drinking water for 2 wk prior to mating until parturition (in utero exposure only) or until weaning (in utero+lactational exposure). At postnatal d 1 (PND1) pups of dams exposed to chloroform had significantly higher serum glucose levels and lower insulin levels, but this effect was not due to b -cell depletion in the neonatal pancreas. Glucose homeostasis in response to a glucose challenge was not changed by chloroform treatment. Chloroform exposure did not affect birthweight; however, offspring of dams exposed to chloroform had significantly impaired postnatal growth. Although fetal and neonatal exposure to chloroform did not elicit physiological changes associated with the onset of type 2 diabetes, there were physiological changes resulting in impaired postnatal growth.

Administration, Oral↗

PubMedDate not supplied

Analytical controls in drug metabolic studies. II. Artifact formation during chloroform extraction of drugs and metabolites with amine substituents.

Chemical artifacts are readily produced during chloroform extractions of drugs and metabolites with amine substituents by the reaction of chloroform contaminants, phosgene and ethyl chloroformate, to form carbamoyl chlorides and carbamates. Chloroform obtained from three different suppliers was examined with regard to the effects of preservatives and exposure to air on the quantity and nature of these contaminants. Extractions with chloroform obtained from a supplier's sealed bottle and containing ethanol preservative produced the least amount of artifact. With previously opened bottles (prior exposure to air, open), the amount of artifact formation rose substantially. Chloroform without preservative or with a nonpolar hydrocarbon preservative likewise produced large amounts of artifacts during extraction. Attempts to purify chloroform showed that distillation was ineffective for the removal of phosgene or ethyl chloroformate, whereas their effective removal was accomplished by solvent elution through a column of activated alumina or upon standing over calcium hydroxide powder. Possible artifact formation must be considered in drug-metabolism studies and appropriate controls included for the detection and elimination of chemical artifacts.

Amines↗

PubMed1999

Competitive Adsorption of Chloroform and Iron Ion onto Activated Carbon Fiber.

Chloroform in tap water has been a significant problem because it may be a carcinogenic substituent. Iron ion exists in tap water because of dissolution from iron water pipes. Iron ions in tap water cause discoloration and a bad odor. The isotherms of chloroform and iron ion adsorption onto activated carbon fibers in a single solution (chloroform or iron ion) and in a binary mixture solution (chloroform and iron ion) were investigated to estimate the competitiveness between chloroform and iron ions. The amount of adsorbed iron ions increased with increasing pore volume of the activated carbon fibers, while that of chloroform decreased. The amount of chloroform adsorbed onto the activated carbon fibers in the binary mixture solution was greater than that in the single solution. These results indicate that the adsorption of chloroform and iron ion onto activated carbon fibers could be competitive. Copyright 1999 Academic Press.

Journal Article↗

PubMed2000

Comparative characterization of CHCl(3) metabolism and toxicokinetics in rodent strains differently susceptible to chloroform-induced carcinogenicity.

A comparative kinetic study in B6C3F1 mice, Osborne-Mendel (OM) and Sprague-Dawley (SD) rats has been undertaken with the major aim to determine the extent of covalent binding of chloroform reactive metabolites produced in vivo through oxidative and/or reductive metabolism in the target organs of chloroform carcinogenicity. Some additional kinetic observations of chloroform biotransformation were also collected comparatively. Expiration of [14C]-CO(2) showed that chloroform metabolism went to saturation in all tested rodent strains. In the B6C3F1 mouse maximal rates of approximately 135 µmol [14C]-CO(2)/kg b.w./h were reached at a dose of approximately 150 mg/kg, while in the two rat strains saturation occurred at a dose of approximately 60 mg/kg, with a maximal rate of approximately 40 µmol [14C]-CO(2)/kg b.w./h. At doses of 150-180 mg/kg b.w., limited differences were found in the distribution and elimination of [14C]-chloroform in the liver and kidney. Species differences have been found in the kinetics of alkali-extractable radioactivity in the blood. The levels of adducts of electrophilic intermediates with the polar heads (PH) of phospholipids (PL) showed a limited variability accross the rodents tested and did not correlate with the species and organ susceptibility to chloroform carcinogenicity. The levels of adducts of radical intermediates with the fatty acyl chains (FC) of PL were much lower than the PH adducts in all the samples analyzed; at the carcinogenicity bioassay doses, statistically significant levels of hepatic FC adducts were present only in the B6C3F1 mouse, where chloroform is hepatocarcinogenic. The observations in the rat kidney were suggestive of the formation of electrophilic reactive metabolites, presumably different from phosgene and associated with an initial chloroform reduction.

Journal Article↗

PubMed1994

Lack of chloroform-induced DNA repair in vitro and in vivo in hepatocytes of female B6C3F1 mice.

Chloroform has been shown to induce hepatocellular carcinomas in female B6C3F1 mice when administered by gavage, but not when given in drinking water. When administered in corn oil at the carcinogenic doses of 238 and 477 mg/kg, chloroform induced necrosis and sustained regenerative cell proliferation in the liver. To investigate the mode of action of tumor induction in the target cells, the ability of chloroform to induce unscheduled DNA synthesis (UDS) was examined in the in vitro and in vivo hepatocyte DNA repair assays. In the in vitro assay, primary hepatocyte cultures from female B6C3F1 mice were incubated with concentrations from 0.01 to 10 mM chloroform in the presence of 3H-thymidine. UDS was assessed by quantitative autoradiography. No induction of DNA repair was observed at any concentration. In the in vivo assay, animals were treated by gavage with 238 and 477 mg/kg chloroform in corn oil. Primary hepatocyte cultures were prepared 2 and 12 hr later, incubated with 3H-thymidine, and assessed for induction of UDS as above. No DNA repair activity was seen at either dose or at either timepoint. These negative results in the target organ are consistent with the concept that neither chloroform nor its metabolites are directly DNA reactive and that the carcinogenicity of chloroform is secondary to induced cytolethality and regenerative cell proliferation.

Administration, Oral↗

PubMed1993

Acute hepatotoxic and nephrotoxic effects of chloroform in male F-344 rats and female B6C3F1 mice.

Previous studies demonstrated that chloroform given by oral gavage in corn oil caused an increased incidence of liver tumors in male and female mice and kidney tumors in male rats, while administration in drinking water resulted in an increased tumor incidence only in the kidneys of the male rats. The tumorigenicity of this nongenotoxic agent has been postulated to be linked with cytolethality and cell proliferation. This study examined the organ-specific toxicity of acute doses of chloroform. Male F-344 rats were given chloroform by gavage in corn oil at the bioassay doses of chloroform of 0 and 180 mg/kg body wt as well as 34 and 477 mg/kg and necropsied 24 hr later. Additional rats were given a single dose of 180 mg chloroform/kg and administered bromodeoxyuridine (BRDU) 2 hr prior to necropsy at 0.5, 1, 2, 4, and 8 days after chloroform treatment. Female B6C3F1 mice were given chloroform by gavage at the bioassay doses of 0, 238, and 477 mg/kg as well as 34 mg/kg and necropsied at 24 hr after treatment. Additional mice were given a single dose of 350 mg chloroform/kg, labeled with BRDU, and necropsied at 0.5, 1, 2, 4, and 8 days after treatment. The kidneys of male rats administered 34, 180, and 477 mg chloroform/kg exhibited mild to severe proximal tubular necrosis in a dose-dependent manner. A 20-fold increase in the labeling index (LI, the percentage of nuclei in S-phase) in the proximal tubule cells was observed 2 days after treatment with the bioassay dose of 180 mg/kg. The livers of male rats exhibited only slight to moderate multifocal centrilobular necrosis at 180 and 477 mg/kg. A 10-fold increase in the LI was observed in the liver of male rats given 477 mg/kg, but no increase was observed at the bioassay dose of 180 mg/kg. In contrast to male rats, female mice developed a dose-dependent centrilobular hepatic necrosis at 238 and 477 mg/kg. No renal lesions were observed in female mice at any dose. A peak increase in LI of 38-fold was observed in hepatocytes in the livers of female mice 2 days after treatment with 350 mg chloroform/kg, with only a 2-fold increase in LI observed in the kidneys. These data indicate that acute chloroform-induced cytolethality leads to increased cell proliferation and that the organ-specific pattern of toxicity is the same as the organ-specific pattern of tumor formation.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗

PubMed1996

A 90-day chloroform inhalation study in F-344 rats: profile of toxicity and relevance to cancer studies.

Chloroform acts via a nongenotoxic-cytotoxic mode of action to produce cancer if given in doses and at dose rates sufficiently high to produce organ-specific toxicity. In a recent study, chloroform failed to induce cancer in male or female F-344 rats when administered by inhalation for 2 years at 90 ppm, 5 days/week. The present study was undertaken to define the concentration-response curves for chloroform-induced lesions and regenerative cell proliferation in the F-344 rat when exposed by inhalation and to correlate those patterns of toxicity with the results from the inhalation cancer bioassay. Male and female F-344 rats were exposed to airborne concentrations of 0, 2, 10, 30, 90, or 300 ppm chloroform 6 hr/day, 7 days/week for 4 days or 3, 6, 13 weeks. Additional treatment groups were exposed 5 days/week for 13 weeks or were exposed for 6 weeks and held until Week 13. Bromodeoxyuridine was administered via osmotic pumps implanted 3.5 days prior to necropsy and the labeling index (LI, percentage of nuclei in S-phase) was evaluated immunohistochemically. A full-screen necropsy identified the kidney, liver, and nasal passages as the only target organs. This study confirmed that 300 ppm is extremely toxic and would be inappropriate for longer-term cancer studies. The primary target in the kidney was the epithelial cells of the proximal tubules of the cortex, with significantly elevated increases in the LI at concentrations of 30 ppm and above. However, only a marginal increase in the renal LI in the males was seen after exposures of 90 ppm, 5 days/week. Chloroform induced hepatic lesions in the midzonal and centrilobular regions with increases in the LI throughout the liver, but only at 300 ppm exposures. An additional liver lesion seen only at the highly hepatotoxic concentration of 300 ppm was numerous intestinal crypt-like ducts surrounded by dense connective tissue. Enhanced bone growth and hypercellularity in the lamina propria of the ethmoid turbinates of the nose occurred at the early time points at concentrations of 10 ppm and above. At 90 days there was a generalized atrophy of the ethmoid turbinates at concentrations of 2 ppm and above. Cytolethality and regenerative cell proliferation are necessary but not always sufficient to induce cancer because of tissue, sex, and species differences in susceptibility. A combination of a lack of direct genotoxic activity by chloroform, only a marginal induction of cell proliferation in the male rat kidney, and lower tissue-specific susceptibility in the female rat is apparently responsible for the reported lack of chloroform-induced cancer in a long-term inhalation bioassay with F-344 rats.

Administration, Inhalation↗

PubMed1999

Metabolism of chloroform by cytochrome P450 2E1 is required for induction of toxicity in the liver, kidney, and nose of male mice.

Chloroform is a nongenotoxic-cytotoxic liver and kidney carcinogen and nasal toxicant in some strains and sexes of rodents. Substantial evidence indicates that tumor induction is secondary to events associated with cytolethality and regenerative cell proliferation. Therefore, pathways leading to toxicity, such as metabolic activation, become critical information in mechanism-based risk assessments. The purpose of this study was to determine the degree to which chloroform-induced cytotoxicity is dependent on the cytochromes P450 in general and P450 2E1 in particular. Male B6C3F(1), Sv/129 wild-type (Cyp2e1+/+), and Sv/129 CYP2E1 knockout (Cyp2e1-/- or Cyp2e1-null) mice were exposed 6 h/day for 4 consecutive days to 90 ppm chloroform by inhalation. Parallel control and treated groups, excluding Cyp2e1-null mice, also received an i.p. injection (150 mg/kg) of the irreversible cytochrome P450 inhibitor 1-aminobenzotriazole (ABT) twice on the day before exposures began and 1 h before every exposure. Cells in S-phase were labeled by infusion of BrdU via an implanted osmotic pump for 3.5 days prior to necropsy, and the labeling index was quantified immunohistochemically. B6C3F(1) and Sv/129 wild-type mice exposed to chloroform alone had extensive hepatic and renal necrosis with significant regenerative cell proliferation. These animals had minimal toxicity in the nasal turbinates with focal periosteal cell proliferation. Administration of ABT completely protected against the hepatic, renal, and nasal toxic effects of chloroform. Induced pathological changes and regenerative cell proliferation were absent in these target sites in Cyp2e1-/- mice exposed to 90 ppm chloroform. These findings indicate that metabolism is obligatory for the development of chloroform-induced hepatic, renal, and nasal toxicity and that cytochrome P450 2E1 appears to be the only enzyme responsible for this cytotoxic-related metabolic conversion under these exposure conditions.

Administration, Inhalation↗

PubMed1999

Time dependence of chloroform-induced metabolic alterations in the liver and kidney of B6C3F1 mice.

The time course of some biochemical changes in the liver and in the kidney was studied in B6C3F1 male mice dosed with a single i.p. injection of 150 mg/kg body weight (b.w.) CHCl(3). Hepatic and renal microsomal cytochrome P450 (P450) content and some related monooxygenase activities, CHCl(3) oxidative and reductive metabolism, cytosolic reduced glutathione (GSH) content and serum markers of nephrotoxicity were measured. In the liver no biochemical changes were produced up to a week after chloroform treatment. On the contrary, the drug-metabolizing enzyme system in the kidney was dramatically and rapidly inactivated by chloroform treatment. Maximum loss of GSH (50%), P450 (80%) and of different enzymatic activities, including CHCl(3) bioactivation, occurred during the first 5 h. These biochemical alterations are early effects, not secondary to morphological tissue changes. Kidney parameters, altered by chloroform treatment, returned to control values at different times: renal function markers became normal in 48 h; GSH levels were recovered at 96 h and the drug-metabolizing enzyme activities at longer times. The present results clearly show that repeated daily doses of chloroform, as those used in carcinogenicity tests, find renal tubular cells not at their physiological status, due to the changes produced by the first chloroform dose. Therefore the similarity in P450-dependent chloroform metabolism shown in vitro by hepatic and renal microsomes from untreated B6C3F1 male mice or in vivo in animals treated once, is lost during repeated treatments. These features should be considered in understanding the different susceptibility of the liver and the kidney to chloroform-induced tumours.

Aniline Hydroxylase↗

PubMed1981

Effect of cysteine, diethyl maleate, and phenobarbital treatments on the hepatotoxicity of [1H]chloroform.

The effects of cysteine, diethyl maleate and phenobarbital treatments and 2H-substitution on the hepatotoxicity of chloroform were investigated. Time course studies of covalent binding and hepatoxicity in phenobarbital-treated rats showed that covalent binding of 14C-label from [14C]chloroform was maximal at 6 h after chloroform administration while hepatotoxicity reached a peak at 18 h. Cysteine treatment reduced both covalent binding and hepatotoxicity, while diethyl maleate and phenobarbital treatments increased both the hepatotoxicity of chloroform and the covalent binding of chloroform metabolites to hepatic proteins. A deuterium isotope effect was present on chloroform-induced hepatotoxicity in diethyl maleate-treated rats suggesting that the previously reported inhibition of haloform metabolism by diethyl maleate occurs at a step in the reaction mechanism after phosgene production. These data support the concept that phosgene is the toxic intermediate in chloroform metabolism.

Alanine Transaminase↗

PubMed1982

Binding of chloroform to mouse and rat hemoglobin.

The covalent binding of chemical carcinogens and mutagens to hemoglobin has been proposed as a dose monitor for environmental exposure. The binding of chloroform to hemoglobin in rats was demonstrated to result from the formation of addition adducts to amino acids in the globin. The altered amino acids were isolated with an amino acid analyzer employing ion exchange chromatography. The covalent binding of orally-administered [14C]chloroform to rat hemoglobin reached a peak within 10 h. Afterwards, the amount of chloroform bound decreased slowly with half remaining at 7 weeks. The extent of chloroform binding was linearly dependent upon dose between 0.1 and 100 mumol/kg. Above 100 mumol/kg chloroform the binding to hemoglobin increased at a reduced rate. The extent of [14C]chloroform binding resulting from either 10 daily doses of 0.1 mumol/kg or a single 1.0 mumol/kg was similar. The binding to hemoglobin in three strains of mice and rats varied from 85 +/- 7 mumol/g Hb for Swiss (CFN) mice to 152 +/- 14 for Fisher-344 rats. We have demonstrated that the binding of chloroform to hemoglobin appears to have the following attributes of a dose monitor: (1) easily accessible from laboratory animals (and humans); (2) dose dependent; (3) stability, so that exposure can be determined weeks after it has ceased; (4) integration of low exposures which individually would be undetectable.

Amino Acids↗

PubMed1996

Levels of myc, fos, Ha-ras, met and hepatocyte growth factor mRNA during regenerative cell proliferation in female mouse liver and male rat kidney after a cytotoxic dose of chloroform.

Chloroform is a liver carcinogen in mice and a kidney carcinogen in rats. It is thought to act through a non-genotoxic-cytotoxic mode of action. Changes in expression of growth control genes accompanying chloroform-induced cytolethality and regeneration may play a part in the development of chloroform-induced tumors. In this experiment, we examined the levels of the myc, fos, Ha-ras, met and hepatocyte growth factor mRNA in livers of female B6C3F(1) mice and kidneys of male F-344 rats to detect changes in gene expression following a single, cytotoxic gavage dose of chloroform in corn oil. Poly A+ RNA was purified from homogenates of livers of mice treated with 350mg/kg chloroform and kidneys of rats treated with 180 mg/kg chloroform and used for Northern blot analysis. Livers of female mice showed large transient increases in levels of myc and fos mRNA while levels of Ha-ras, met and the hepatocyte growth factor gene mRNA remained near control levels. In the male rat kidney, levels of myc mRNA increased after treatement, while levels of mRNA of all other genes examined remained near control levels. This pattern of gene expression is consistent with that induced by other cytotoxic carcinogens and suggest that alteration of the myc and fos genes could be involved in the regenerative cell proliferation that ultimately could play a role in chloroform-induced tumors.

Animals↗

PubMed1996

Comparison of chloroform-induced toxicity in the kidneys, liver, and nasal passages of male Osborne-Mendel and F-344 rats.

Chloroform given by gavage in corn oil at 180 mg/kg per day induced kidney tumors in male Osborne-Mendel rats. Chloroform-induced cytotoxicity and regenerative cell proliferation have been observed in the kidneys of male F-344 rats. In order to compare the acute sensitivity of male Osborne-Mendel with F-344 rats, animals from both strains were administered a single gavage dose of 0, 10, 34, 90, 180, or 477 mg/kg chloroform and necropsied 48 h later. Known target tissues were examined for histological changes. Regenerative cell proliferation was assessed as a labeling index (LI, percent of cells in S-phase) as determined by nuclear incorporation of bromodeoxyuridine. The epithelial cells of the proximal tubules of the kidney cortex were the primary target cells for cytotoxicity and regenerative cell proliferation. A dose-dependent increase in the LI was present in the kidney of Osborne-Mendel rats given doses of 10 mg/kg chloroform and above and in F-344 rats given 90 mg/kg and above. The maximal increase in the LI was 4.5- or 3.7-fold over control in Osborne-Mendel or F-344 given 477 mg/kg, respectively. The only increase in the hepatocyte LI was in the F-344 rats given 477 mg/kg. Edema and periosteal hypercellularity were observed in the nasal passages of both strains at doses of 90 mg/kg and above. These data indicate that Osborne-Mendel and F-344 rats are about equally susceptible to chloroform-induced nephrotoxicity. These results provide a basis for linking the extensive data base on mechanisms of action of chloroform toxicity in F-344 rats to the Osborne-Mendel rat and support the hypothesis that events secondary to chloroform-induced cytolethality and regenerative cell proliferation played a role in the induction of renal tumors in the Osborne-Mendel rat.

Animals↗