A modified gelatin zymography technique incorporating total protein normalization.

Gelatinase zymography is a commonly used laboratory procedure; however, variability in sample loading and concentration reduce the accuracy of quantitative results obtained from this technique. To facilitate normalization of gelatinase activity by loaded protein amount, we developed a protocol using the trihalocompound 2,2,2-trichloroethanol to allow for gelatin zymography and total protein labeling within the same gel. We showed that detected protein levels increased linearly with loading, and describe a loading concentration range over which normalized gelatinase activity was constant. We conclude that in-gel total protein detection is feasible in gelatin zymography and greatly improves comparison of gelatinase activity between samples.

Comparative analysis of the relationship between trichloroethylene metabolism and tissue-specific toxicity among inbred mouse strains: liver effects.

Trichloroethylene (TCE) is a widely used organic solvent. Although TCE is classified as carcinogenic to humans, substantial gaps remain in our understanding of interindividual variability in TCE metabolism and toxicity, especially in the liver. A hypothesis was tested that amounts of oxidative metabolites of TCE in mouse liver are associated with hepatic-specific toxicity. Oral dosing with TCE was conducted in subacute (600 mg/kg/d; 5 d; 7 inbred mouse strains) and subchronic (100 or 400 mg/kg/d; 1, 2, or 4 wk; 2 inbred mouse strains) designs. The quantitative relationship was evaluated between strain-, dose-, and time-dependent formation of TCE metabolites from cytochrome P-450-mediated oxidation (trichloroacetic acid [TCA], dichloroacetic acid [DCA], and trichloroethanol) and glutathione conjugation [S-(1,2-dichlorovinyl)-L-cysteine and S-(1,2-dichlorovinyl)glutathione] in serum and liver, and various hepatic toxicity phenotypes. In subacute study, interstrain variability in TCE metabolite amounts was observed in serum and liver. No marked induction of Cyp2e1 protein levels in liver was detected. Serum and hepatic levels of TCA and DCA were correlated with increased transcription of peroxisome proliferator-marker genes Cyp4a10 and Acox1 but not with degree of induction in hepatocellular proliferation. In subchronic study, serum and liver levels of oxidative metabolites gradually decreased over time despite continuous dosing. Hepatic protein levels of CYP2E1, ADH, and ALDH2 were unaffected by treatment with TCE. While the magnitude of induction of peroxisome proliferator-marker genes also declined, hepatocellular proliferation increased. This study offers a unique opportunity to provide a scientific data-driven rationale for some of the major assumptions in human health assessment of TCE.

Comparative analysis of the relationship between trichloroethylene metabolism and tissue-specific toxicity among inbred mouse strains: kidney effects.

Trichloroethylene (TCE) is a well-known environmental and occupational toxicant that is classified as carcinogenic to humans based on the epidemiological evidence of an association with higher risk of renal-cell carcinoma. A number of scientific issues critical for assessing human health risks from TCE remain unresolved, such as the amount of kidney-toxic glutathione conjugation metabolites formed, interspecies and interindividual differences, and the mode of action for kidney carcinogenicity. It was postulated that TCE renal metabolite levels are associated with kidney-specific toxicity. Oral dosing with TCE was conducted in subacute (600 mg/kg/d; 5 d; 7 inbred mouse strains) and subchronic (100 or 400 mg/kg/d; 1, 2, or 4 wk; 2 inbred mouse strains) designs. The quantitative relationship was evaluated between strain-, dose, and time-dependent formation of TCE metabolites from cytochrome P-450-mediated oxidation (trichloroacetic acid [TCA], dichloroacetic acid [DCA], and trichloroethanol) and glutathione conjugation [S-(1,2-dichlorovinyl)-L-cysteine and S-(1,2-dichlorovinyl)glutathione], and various kidney toxicity phenotypes. In subacute study, interstrain differences in renal TCE metabolite levels were observed. In addition, data showed that in several strains kidney-specific effects of TCE included induction of peroxisome proliferator-marker genes Cyp4a10 and Acox1, increased cell proliferation, and expression of KIM-1, a marker of tubular damage and regeneration. In subchronic study, peroxisome proliferator-marker gene induction and renal toxicity diminished while cell proliferative response was elevated in a dose-dependent manner in NZW/LacJ but not C57BL/6J mice. Overall, data demonstrated that renal TCE metabolite levels are associated with kidney-specific toxicity and that these effects are strain dependent.

Protective effects of fomepizole on 2-chloroethanol toxicity.

2-Chloroethanol (2-CE) is a widely used industrial solvent. In Taiwan, Taiwanese farmers apply 2-CE on grape-vines to accelerate grape growth, a practice that in some cases have caused poisoning in humans. Thus, there is strong interest in identifying antidotes to 2-CE. This study examines the protective role in 2-CE intoxicated rats. Alcohol dehydrogenase and glutathione were hypothesized to be important in the metabolism of 2-CE. This study used fomepizole, an alcohol dehydrogenase inhibitor, and chemicals that affected glutathione metabolism to study 2-CE toxicity. Notably, fomepizole 5 mg/kg significantly increased median lethal dose (LD(50)) of 2-CE from 65.1 to 180 mg/kg and reduced the production of a potential toxic metabolite chloroacetaldehyde (CAA) in animal plasma. In contrast, disulfiram (DSF), an aldehyde dehydrogenase inhibitor, increased the toxicity of 2-CE on the lethality in rats. Additional or pretreatment with N-acetylcysteine (NAC) and fomepizole significantly reduced plasma CAA concentrations. Fomepizole also significantly reduced 2-CEinhibited glutathione activity. Otherwise, pretreatment with NAC for 4 days followed by co-treatment with fomepizole significantly decreased formation of the metabolic CAA. These results indicated that its catalytic enzyme might play a vital role during 2-CE intoxication, and the combination of fomepizole and NAC could be a protective role in cases of acute 2-CE intoxication.

Solubility of toluene, benzene and TCE in high-microbial concentration systems.

We report measurements of solubility limits for benzene, toluene, and TCE in systems that contain varying levels of biomass up to 0.13 g mL(-1) for TCE and 0.25 g mL(-1) for benzene and toluene. The solubility limit increased from 21 to 48 mM when biomass (in the form of yeast) was added to aqueous batch systems containing benzene. The toluene solubility limit increased from 4.9 to greater than 20mM. For TCE, the solubility increased from 8mM to more than 1000 mM. Solubility for TCE (trichloroethylene) was most heavily impacted by biomass levels, changing by two orders of magnitude as the microbial concentrations approach those in biofilms.

Mechanistics of trichloroethylene mineralization by the white-rot fungus Trametes versicolor.

The white-rot fungus Trametes versicolor degraded trichloroethylene (TCE), a highly oxidized chloroethene, and produced 2,2,2-trichloroethanol and carbon dioxide as the main products of degradation, based on the results obtained using [13C]-TCE as the substrate. For a range of concentrations of TCE between 2 and 20 mg l(-1), 53% of the theoretical maximum chloride expected from complete degradation of TCE was observed. Laccase was shown to be induced by TCE, but did not appear to play a role in TCE degradation. Cytochrome P-450 appears to be involved in TCE degradation, as evidenced by marked inhibition of degradation of TCE in the presence of 1-aminobenzotriazole, a known inhibitor of cytochrome P-450. Our results suggested that chloral (trichloroacetaldehyde) was an intermediate of the TCE degradation pathway. The results indicate that the TCE degradation pathway in T. versicolor appears to be similar to that previously reported in mammals and is mechanistically quite different from bacterial TCE degradation.

Lack of formic acid production in rat hepatocytes and human renal proximal tubule cells exposed to chloral hydrate or trichloroacetic acid.

The industrial solvent trichloroethylene (TCE) and its major metabolites have been shown to cause formic aciduria in male rats. We have examined whether chloral hydrate (CH) and trichloroacetic acid (TCA), known metabolites of TCE, produce an increase in formic acid in vitro in cultures of rat hepatocytes or human renal proximal tubule cells (HRPTC). The metabolism and cytotoxicity of CH was also examined to establish that the cells were metabolically active and not compromised by toxicity. Rat hepatocytes and HRPTC were cultured in serum-free medium and then treated with 0.3-3mM CH for 3 days or 0.03-3mM CH for 10 days, respectively and formic acid production, metabolism to trichloroethanol (TCE-OH) and TCA and cytotoxicity determined. No increase in formic acid production in rat hepatocytes or HRPTC exposed to CH was observed over and above that due to chemical degradation, neither was formic acid production observed in rat hepatocytes exposed to TCA. HRPTC metabolized CH to TCE-OH and TCA with a 12-fold greater capacity to form TCE-OH versus TCA. Rat hepatocytes exhibited a 1.6-fold and three-fold greater capacity than HRPTC to form TCE-OH and TCA, respectively. CH and TCA were not cytotoxic to rat hepatocytes at concentrations up to 3mM/day for 3 days. With HRPTC, one sample showed no cytotoxicity to CH at concentrations up to 3mM/day for 10 days, while in another cytotoxicity was seen at 1mM/day for 3 days. In summary, increased formic acid production was not observed in rat hepatocytes or HRPTC exposed to TCE metabolites, suggesting that the in vivo response cannot be modelled in vitro. CH was toxic to HRPTC at millimolar concentrations/day over 10 days, while glutathione derived metabolites of TCE were toxic at micromolar concentrations/day over 10 days [Lock, E.A., Reed, C.J., 2006. Trichloroethylene: mechanisms of renal toxicity and renal cancer and relevance to risk assessment. Toxicol. Sci. 19, 313-331] supporting the view that glutathione derived metabolites are likely to be responsible for nephrotoxicity.

Application of cryopreserved human hepatocytes in trichloroethylene risk assessment: relative disposition of chloral hydrate to trichloroacetate and trichloroethanol.

BACKGROUND: Trichloroethylene (TCE) is a suspected human carcinogen and a common groundwater contaminant. Chloral hydrate (CH) is the major metabolite of TCE formed in the liver by cytochrome P450 2E1. CH is metabolized to the hepatocarcinogen trichloroacetate (TCA) by aldehyde dehydrogenase (ALDH) and to the noncarcinogenic metabolite trichloroethanol (TCOH) by alcohol dehydrogenase (ADH). ALDH and ADH are polymorphic in humans, and these polymorphisms are known to affect the elimination of ethanol. It is therefore possible that polymorphisms in CH metabolism will yield subpopulations with greater than expected TCA formation with associated enhanced risk of liver tumors after TCE exposure. METHODS: The present studies were undertaken to determine the feasibility of using commercially available, cryogenically preserved human hepatocytes to determine simultaneously the kinetics of CH metabolism and ALDH/ADH genotype. Thirteen human hepatocyte samples were examined. Linear reciprocal plots were obtained for 11 ADH and 12 ALDH determinations. RESULTS: There was large interindividual variation in the Vmax values for both TCOH and TCA formation. Within this limited sample size, no correlation with ADH/ALDH genotype was apparent. Despite the large variation in Vmax values among individuals, disposition of CH into the two competing pathways was relatively constant. CONCLUSIONS: These data support the use of cryopreserved human hepatocytes as an experimental system to generate metabolic and genomic information for incorporation into TCE cancer risk assessment models. The data are discussed with regard to cellular factors, other than genotype, that may contribute to the observed variability in metabolism of CH in human liver.

Increased formic acid excretion and the development of kidney toxicity in rats following chronic dosing with trichloroethanol, a major metabolite of trichloroethylene.

The chronic toxicity of trichloroethanol, a major metabolite of trichloroethylene, has been assessed in male Fischer rats (60 per group) given trichloroethanol in drinking water at concentrations of 0, 0.5 and 1.0 g/l for 52 weeks. The rats excreted large amounts of formic acid in urine reaching a maximum after 12 weeks ( approximately 65 mg/24 h at 1 g/l) and thereafter declining to reach an apparent steady state at 40 weeks (15-20 mg/24 h). Urine from treated rats was more acidic throughout the study and urinary methylmalonic acid and plasma N-methyltetrahydrofolate concentrations were increased, indicating an acidosis, vitamin B12 deficiency and impaired folate metabolism, respectively. The rats treated with trichloroethanol developed kidney damage over the duration of the study which was characterised by increased urinary NAG activity, protein excretion (from 4 weeks), increased basophilia, protein accumulation and tubular damage (from 12 to 40 weeks), increased cell replication (at week 28) and evidence in some rats of focal proliferation of abnormal tubules at 52 weeks. It was concluded that trichloroethanol, the major metabolite of trichloroethylene, induced nephrotoxicity in rats as a result of formic acid excretion and acidosis.

Trichloroethylene oxidative metabolism in plants: the trichloroethanol pathway.

Trichloroethylene (TCE) is a widespread and persistent environmental contaminant. Recently, plants, poplar trees in particular, have been investigated as a tool to remove TCE from soil and groundwater. The metabolism of TCE in plants is being investigated for two reasons: one, plant uptake and metabolism represent an important aspect of the environmental fate of the contaminant; two, metabolism pattern and metabolite identification will help assess the applicability of phytoremediation. It was previously shown that TCE metabolites in plants are similar to ones that result from cytochrome P450-mediated oxidation in mammals: trichloroethanol, trichloroacetate and dichloroacetate. Our measurements indicate that one of these metabolites, trichloroethanol, is further glycosylated in tobacco and poplar. The glycoside was detected in all tissues (roots, stems and leaves) in comparable levels, and was at least 10 fold more abundant than free trichloroethanol. The glycoside in tobacco was identified as the ss-D-glucoside of trichloroethanol by comparison of the mass spectra and the chromatographic retention time of its acetylation product to that of the synthesized standard. Trichloroethanol and its glucoside did not persist in plant tissue once plants are removed from TCE contaminated water, indicating further metabolism.

Species- and sex-related differences in metabolism of trichloroethylene to yield chloral and trichloroethanol in mouse, rat, and human liver microsomes.

Trichloroethylene (TRI) has been shown to cause a variety of tumors, particularly in mouse liver and lung and rat kidney. However, a clear association between exposure to TRI and cancer development in humans has not been established. Because TRI metabolism by cytochrome P450s has been implicated in the mechanisms of TRI-induced carcinogenicity in mice, the purpose of the present study was to characterize the kinetics of TRI oxidation in male and female mouse, rat, and human liver microsomes to possibly allow for a better assessment of human risk. Methods were developed to detect and quantitate chloral, trichloroethanol, trichloroacetic acid, dichloroacetic acid, chloroacetic acid, glyoxylic acid, and oxalic acid, known TRI metabolites in rodents or humans. However, only chloral and its further metabolite, trichloroethanol, were consistently detected in the various liver microsomes in the presence of NADPH. Chloral was the major metabolite detected, and its levels were species- and sex-dependent; the amounts of trichloroethanol detected were also species- and sex-dependent but never exceeded 15% of total metabolites. Double-reciprocal plots of metabolite formation with male and female rat and human liver microsomes indicated biphasic kinetics, but this trend was not observed with microsomes from male or female mouse liver. The Vmax data are consistent, with male and female mice being more susceptible to TRI-induced liver carcinogenicity than male rats. However, the Vmax/Km ratios in male and female rat liver microsomes, in comparison with the male mouse liver microsomes, did not correlate with tumor incidences in these tissues. Furthermore, as only two out of six human liver samples examined exhibited Vmax/Km ratios similar or higher than the ratio obtained with male mouse liver, humans may vary in their toxic response after TRI exposure.

Trichloroethylene-induced mouse lung tumors: studies of the mode of action and comparisons between species.

CD-1 mice exposed to 450 ppm trichloroethylene, 6 hr/day, 5 days/week, for 2 weeks showed a marked vacuolation of lung Clara cells after the first exposure of each week and a marked increase in cell division after the last exposure of each week. The damage seen in mouse lung Clara cells is caused by an accumulation of chloral resulting from high rates of metabolism of trichloroethylene but poor clearance of chloral to trichloroethanol and its glucuronide. The activity and distribution of the key metabolizing enzymes in this pathway have been compared in mouse, rat, and human lung. While mouse lung microsomal fractions were able to metabolize trichloroethylene to chloral at significant rates, the rate in rat lung was 23-fold lower and a rate could not be detected in human lung microsomes at all. Immunolocalization of cytochrome P450IIE1 in lung sections revealed high concentrations in mouse lung Clara cells with lesser amounts in type II cells. Lower levels of enzyme could be detected in Clara cells of rat lung, but not at all in human lung sections. Western blots of lung tissues from the three species and of mouse lung Clara cells were entirely consistent with these observations. Consequently, it is highly unlikely that humans exposed to trichloroethylene are at risk from the lung damage/cell proliferation mechanism that is believed to lead to the development of tumors in the mouse lung.

N-acetyl-S-(1,2,2-trichlorovinyl)-L-cysteine and 2,2,2-trichloroethanol: two novel metabolites of tetrachloroethene in humans after occupational exposure.

The excretion of tetrachloroethene metabolites in urine was studied in occupationally exposed workers to identify and quantify metabolites formed by glutathione conjugation and by cytochrome P450 oxidation of tetrachloroethene in humans. The glutathione conjugation pathway has been implicated in the chronic toxicity and possible tumorigenicity of tetrachloroethene to the kidney in rats. The biosynthesis of S-(1,2,2-trichlorovinyl)glutathione and N-acetyl-S-(1,2,2-trichlorovinyl)-L-cysteine in humans had not been demonstrated. In this study, we investigated the biotransformation of tetrachloroethene in humans occupationally exposed during dry cleaning. Tetrachloroethene concentrations in the air of the dry cleaning shop were 50 +/- 4 ppm; two individuals were exposed for 8 hr daily and two individuals were exposed for 4 hr daily. In urine samples collected from the individuals at the beginning and at the end of the work week, N-acetyl-S-(1,2,2-trichlorovinyl)-L-cysteine and 2,2,2-trichloroethanol as tetrachloroethene metabolites in humans were identified by GC/MS. The concentrations of N-acetyl-S-(1,2,2-trichlorovinyl)-L-cysteine in the urine of the individuals were not significantly different at the start and at the end of the work week; however, concentrations of both N-acetyl-S-(1,2,2-trichlorovinyl)-L-cysteine and 2,2,2-trichloro compounds (trichloroacetic acid and 2,2,2-trichloroethanol) as a marker for cytochrome P450-mediated metabolism were proportional to the length of daily tetrachloroethene exposure. A remarkable difference in the excretion pattern of 2,2,2-trichloro compounds, the major tetrachloroethene metabolites, was observed. Trichloroacetic acid and 2,2,2-trichloroethanol were present in the urine of two of the exposed individuals. Only 2,2,2-trichloroethanol was identified as a major urinary tetrachloroethene metabolite in two other individuals who did not excrete detectable amounts of trichloroacetic acid. The obtained results indicate that humans also have the ability to biosynthesize nephrotoxic glutathione S-conjugates from tetrachloroethene; however, when compared with rats, the human capacity for the biosynthesis of N-acetyl-S-(1,2,2-trichlorovinyl)-L-cysteine seems to be lower.

Mouse liver microsomal metabolism of chloral hydrate, trichloroacetic acid, and trichloroethanol leading to induction of lipid peroxidation via a free radical mechanism.

Metabolism of chloral hydrate (CH) by male B6C3F1 mouse liver microsomes (control-microsomes) generated free radical intermediates that resulted in endogenous lipid peroxidation, forming malondialdehyde (MDA), formaldehyde (FA), acetaldehyde (ACT), acetone, and propionaldehyde. Because MDA, FA, and ACT are tumorigens, endogenous formation of lipid peroxidation products via a free radical mechanism may be responsible for hepatocellular tumorigenicity of CH to the B6C3F1 mice. Trichloroacetic acid (TCA) and trichloroethanol (TCE), the primary metabolites of CH, also generated free radicals and induced lipid peroxidation. Lipid peroxidation from TCA equaled that induced by CH, whereas that from TCE was 3- to 4-fold lower, suggesting that metabolism of CH to TCA may be the predominant pathway leading to lipid peroxidation. Metabolism of CH, TCA, and TCE by liver microsomes of mice pretreated with pyrazole (pyrazole-microsomes) yielded lipid peroxidation products at a level 2- to 3-fold higher than those from liver microsomes of untreated mice. In addition, CH-induced lipid peroxidation catalyzed by control-microsomes and pyrazole-microsomes was reduced significantly by 2,4-dichloro-6-phenylphenoxyethylamine, a general cytochrome P450 inhibitor. Thus, our study suggests that cytochrome P450 is the enzyme catalyzing the metabolic activation of CH and its metabolites (TCA and TCE) leading to lipid peroxidation, and that CYP2E1 may be the major isozyme responsible. This latter conclusion was supported by results using human lymphoblastoid cells expressing cytochrome P4502E1, which metabolized CH to reactants inducing mutations, whereas the parental cell line was inactive.

Formation of malondialdehyde-modified 2'-deoxyguanosinyl adduct from metabolism of chloral hydrate by mouse liver microsomes.

We previously reported that metabolism of chloral hydrate (CH), a widely used sedative and hypnotic, by male B6C3F1 mouse liver microsomes resulted in lipid peroxidation, producing the tumorigen malondialdehyde (MDA). Now we have found that incubation of CH in the presence of calf thymus DNA resulted in the formation of an MDA-modified DNA adduct as detected by 32P-postlabeling analysis. Similar results were obtained from incubation of trichloroacetic acid and trichloroethanol, both metabolites of CH.

Factors affecting species differences in the kinetics of metabolites of trichloroethylene.

The hepatocarcinogenicity of trichloroethylene (TRI) in mice has been attributed to a metabolite, trichloroacetate (TCA). Rats of various strains appear to be resistant to TRI-induced hepatocarcinogenesis and produce lower peak concentrations of TCA. Mice, however, also form significant amounts of another carcinogenic metabolite, dichloroacetate (DCA). The present study was conducted to investigate the interspecies differences in the metabolism of TRI between the mouse, rat, and dog and to gain further insight into the role metabolic factors may play in the apparent species specificity of liver tumor induction by TRI. Fischer 344 rats and beagle dogs were dosed orally with TRI and blood was analyzed for TRI, DCA, TCA, and trichloroethanol (TCE). Data on the metabolism of TRI in mice have been previously published. Limited data are available on the metabolism of TRI in humans. Dogs produce higher peak concentrations and have a larger area under the concentration-time curve (AUC) for TCA as compared to rats given similar doses of TRI. Dichloroacetate was not found in measurable concentrations, that is, above 4 nmol/ml, the minimal quantifiable concentration, in the blood of either rats or dogs. Appreciable concentrations of DCA were found in the blood of mice administered TRI in previous studies. Trichloroethanol was found to be present in the blood, urine, and bile, primarily as the glucuronide conjugate. In all species, peak TCA concentrations were observed beyond the disappearance of TRI. The AUC for TCE glucuronide is consistent with its acting as a precursor for TCA and probably contributes to the continued increase in TCA concentration after TRI disappears from the system. Investigations into the binding of TCA to plasma constituents in the rat, dog, mouse, and human suggest that binding also plays a role in species differences in the distribution and elimination of TCA.

Urinary methylchloroform rather than urinary metabolites as an indicator of occupational exposure to methylchloroform.

In order to compare methylchloroform (MC, or 1,1,1-trichloroethane) per se and its metabolites in urine as indicators of occupational exposure to this solvent, 50 male solvent workers were studied in the second half of a working week to evaluate the exposure-excretion relationship. The time-weighted average intensity of solvent exposure of individuals during an 8-h shift was monitored by personal diffusive sampling. Urine samples were collected near the end of the shift and were analyzed for MC and its metabolites [i.e., trichloroacetic acid (TCA), trichloroethanol (TCE) and total trichloro-compounds (TTC; the sum of TCA and TCE)] by head-space gas chromatography. MC per se, TCA, TCE, and TTC in urine correlated significantly (P < 0.01) with MC in ambient air, and among the four the correlation coefficient was highest for MC. The same result were obtained by multiple regression analysis in which ambient air MC was taken as the dependent variable and either the three indicators urinary MC, TCA, and TCE or the two indicators urinary MC and TTC were taken as independent variables. Taking the specificity and selectivity of the analyte as well as the simple and hazardous chemical-free procedure of analysis into consideration, it is concluded that MC is the analyte of choice as an indicator of occupational exposure to MC, when urine is selected as a specimen available by noninvasive sampling.

The role of tryptophanyl residues in electron transfer from NADPH--adrenodoxin reductase to adrenodoxin.

Chemical modification of tryptophanyl residues of NADPH - adrenodoxin reductase by N - bromosuccinimide and trichloroethanol prevents the interaction of the enzyme with adrenodoxin. The modification does not touch other amino acid residues besides tryptophan (tyrosine, lysine and cysteine) or disturb the structure of protein. The presence of adrenodoxin suppresses the modification. The data obtained indicate the participation of adrenodoxin reductase tryptophan residues in the interaction with adrenodoxin.

Effect of ethanol on the metabolism of trichloroethylene.

Trichloroethylene (TCE) is metabolized to chloral hydrate (CH) by the cytochrome P-450 monooxygenase system. CH can either be oxidized by chloral hydrate dehydrogenase to trichloroacetic acid (TCA) or reduced by alcohol dehydrogenase to trichloroethanol (TCEtOH). The oxidation reaction requires NAD+, while the reduction reaction requires NADH. Since ethanol (EtOH) is known to alter the NAD+/NADH ratio in the hepatocyte, it was coadministered with TCE in an attempt to alter the metabolism of TCE. This would provide a means for predicting interactions of ethanol on the hepatotoxicity and carcinogenicity of TCE. Male Sprague-Dawley rats were administered oral doses of either 1.52, 4.56, or 22.8 mmol/kg TCE, with the treatment group receiving an additional 1.52, 4.56, or 22.8 mmol/kg EtOH, respectively. Blood and urine samples were collected over 72 h. The clearance of TCE appeared to be saturated at the 4.56 mmol/kg dose, as evidenced by prolonged residence times for TCE in the body. Consistent with this result, there was an attenuation of the increases in the levels of TCEtOH and TCA in blood. However, the time to peak concentration of these metabolites was delayed with increasing doses and their residence time in the body was prolonged. Therefore, the area under the curve (AUC) for TCEtOH and TCA continued to increase with the higher doses of TCE. Measurement of the net output of these metabolites in urine confirmed that, although metabolism was saturated, the net metabolic conversion of TCE increased. As predicted, EtOH decreased blood levels of TCA, but only at early times at the high dose. EtOH did increase the urinary TCEtOH/TCA ratio at all dose levels. These results are consistent with the hypothesis of a more reduced state in the hepatocyte caused by the generation of excessive reducing equivalents by EtOH metabolism. The metabolism of TCE is shifted toward reduction to TCEtOH, away from oxidation to TCA. However, the effect was prominent only at extremely high doses of TCE and EtOH.

2,2,2-Trifluoroethanol intestinal and bone marrow toxicity: the role of its metabolism to 2,2,2-trifluoroacetaldehyde and trifluoroacetic acid.

2,2,2-Trifluoroethanol (TFE) produces bone marrow and small intestine toxicity resulting in leukopenia, loss of intestinal dry weight, and consequent lethal septicemia in male Wistar rats. Its metabolic pathway, based on serum and small intestine time courses of substrate and metabolites, was determined to be TFE in equilibrium 2,2,2-trifluoroacetaldehyde (TFAld)----trifluoroacetic acid (TFAA). Administered TFE and TFAld were not toxic per se, since their toxicity and metabolism were inhibited by pyrazole. TFE and TFAld were equipotent at equimolar doses thus precluding the oxidative reaction, TFE to TFAld, from being the toxic step. Since equimolar TFAA exhibited no toxic effects, an oxidative intermediate on the pathway from TFAld to TFAA, most likely F3C-C+(OH)2, must thus be the toxic moiety. The intermediate TFAld is stable in serum, as determined by a novel assay developed for its analysis in biological systems, and can be transported to the target tissues, bone marrow, and small intestine, after formation probably in the liver. On the basis of the more rapid metabolism of TFE to higher levels of TFAld in the small intestine and bone marrow than in the serum, the closer correspondence of bone marrow and small intestine metabolite ratios than serum ratios at high and low doses of TFE to the corresponding ratios of toxicity, and the decreased toxicity of TFAld when administered ig versus ip, the formation of the toxic metabolic intermediate of TFE probably occurs in the target tissues.