The metabolite ratio as a function of chloral hydrate dose and intracellular redox state in the perfused rat liver

Chloral hydrate (CH), an intermediate metabolite of trichloroethylene, is reduced to trichloroethanol (TCE) by alcohol dehydrogenase and aldehyde reductase, and is also oxidized to trichloroacetic acid (TCA) by the nicotinamide adenine dinucleotide (NAD)-dependent enzyme, CH dehydrogenase. Alcohol dehydrogenase requires reduced NAD (NADH), aldehyde reductase requires reduced nicotinamide adenine dinucleotide phosphate (NADPH) and CH dehydrogenase requires NAD to complete the reaction. It is unclear which reaction is predominant at the physiological redox level in intact liver cells. To study this question, we perfused the livers of well-fed rats with Krebs-Ringer buffer solution containing 0.1 mM pyruvate/1.0 mM lactate. The levels of TCE and TCA in the effluent were measured by gas chromatography, and the fluorescence of reduced pyridine nucleotides was measured with a surface fluorometer. When a low concentration (below 0.25 mM) of CH was administered, more TCA than TCE was produced. When a high concentration of CH was administered (over 0.5 mM), TCE production was greater. Reduced pyridine nucleotides decreased inversely with the CH concentration. Even at low CH concentrations, pyridine nucleotides were not reduced. When 10 mM lactate was added to the perfusate in order to reduce the pyridine nucleotides in the liver cells, the TCE/TCA ratio increased. On the other hand, the TCE/TCA ratio tended to fall following the addition of 5.0 mM pyruvate. In conclusion, the TCE/TCA ratio was altered according to the concentration of CH, and to the redox level of pyridine nucleotides in the liver.     

Species differences in the metabolism of trichloroethylene to the carcinogenic metabolites trichloroacetate and dichloroacetate.

Differing rates and extent of trichloroethylene (TCE) metabolism have been implicated as being responsible for varying sensitivities of mice and rats to the hepatocarcinogenic effects of TCE. Recent data indicate that the induction of hepatic tumors in mice may be attributed to the metabolites trichloroacetate (TCA) and/or dichloroacetate (DCA). The present study was directed at determining whether mice and rats varied in (1) the peak blood concentrations, (2) the area under the blood concentration over time curves (AUC) for TCE and metabolites in blood, and (3) the net excretion of TCE to these metabolites in urine in the dose range used in the cancer bioassays of TCE, and to contrast the kinetic parameters observed for TCE-derived TCA and DCA with those obtained following direct administration of TCA and DCA. Blood and urine samples were collected over 72 hr from rats and mice after a single oral dose of TCE of 1.5 to 23 mmol/kg. The AUC values from the blood concentration with time profiles of TCE, TCA, and trichloroethanol (TCOH) were similar for Sprague-Dawley rats and B6C3F1 mice. Likewise, the percentages of initial TCE dose recovered as the urinary metabolites TCA and TCOH were comparable. Nevertheless, the peak blood concentrations of TCE, TCA, and TCOH observed in mice were much greater than those in rats, while the residence time of TCE and metabolites was prolonged in rats relative to that of mice. DCA was detected in the blood of mice but not in rats. The blood concentrations of DCA observed in mice given a carcinogenic dose of TCE (15 mmol/kg) were of the same magnitude as those observed with carcinogenic doses of DCA. In conclusion, the net metabolism of TCE to TCA and TCOH was similar in rats and mice. The initial rates of metabolism of TCE to TCA, however, were much higher in mice, especially as the TCE dose was increased, leading to greater concentrations of TCA and DCA in mice approximated those produced by carcinogenic doses of the chlorinated acetates makes it highly likely that both compounds play a role in the induction of hepatic tumors in mice by TCE.     

Induction of strand breaks in DNA by trichloroethylene and metabolites in rat and mouse liver in vivo

The ability of trichloroethylene (TCE) and selected metabolites to induce single-strand breaks in hepatic DNA of male B6C3F1 mice and Sprague-Dawley rats in vivo was evaluated using an alkaline unwinding assay. Doses of TCE of 22-30 mmol/kg were required to produce strand breaks in DNA in rats, whereas a dose of 11.4 mmol/kg was sufficient to increase the rate of alkaline unwinding in mice. To assess the importance of TCE metabolism to this response, rats were subjected to pretreatments of ethanol, phenobarbital, TCE, or the appropriate vehicle for 4 days prior to challenge doses of TCE. Phenobarbital and TCE, but not ethanol pretreatments, reduced the dose of TCE required to produce significant increases in single-strand breaks. In another series of experiments, mice and rats were treated with metabolites of TCE. Trichloroacetate, dichloroacetate, and chloral hydrate induced strand breaks in hepatic DNA in a dose-dependent manner in both species. Strand breaks in DNA were observed at doses that produced no observable hepatotoxic effects as measured by serum aspartate aminotransferase and alanine aminotransferase levels. The slopes of the dose-response curves and the order of potency of these metabolites differed significantly between rats and mice, suggesting that different mechanisms of single-strand break induction may be involved in the two species. These data provide a potential explanation for the different sensitivity of mice and rats to the hepatocarcinogenic effects of TCE.     

The metabolism of trichloroethylene and its metabolites in the perfused liver

The metabolism of trichloroethylene (TRI) and its metabolites, chloral hydrate (CH), trichloroethanol (free-TCE) and trichloroacetic acid (TCA), were examined in the isolated perfused rat liver, to clarify the role of the liver in the metabolism of TRI. TRI was rapidly converted to TCE and TCA by the perfused liver. TCA was produced from TRI about 2.5 times greater than was total-TCE. CH was metabolized to TCE and TCA immediately. TCA was also a dominant metabolite of CH over total-TCE. TCE(free type) was speedily conjugated by the liver. A portion of TCE was converted to TCA. Less than 10% of these metabolites produced by the liver were excreted into the bile. Most of them appeared in the perfusate.     

Metabolism of chloral hydrate in the anoxic perfused liver

The metabolism of chloral hydrate (CH) under anoxic conditions was investigated in the non-recirculating, hemoglobin-free liver perfusion system. CH uptake in the anoxic liver decreased to about 80% of that in the oxygen-supplied liver. The reduction of CH to trichloroethanol (TCE) increased and the oxidation of CH to trichloroacetic acid (TCA) decreased. The TCE/TCA ratio increased; however, the total trichloro compounds, that is TCE and TCA, were not significantly altered by anoxia. Though approximate 14% of the CH infused into the oxygen-supplied liver was changed to substances other than TCE or TCA, the unknown part was a very small portion in the anoxic liver. The decrease in CH uptake, by the anoxic liver, is thought to be equivalent to the decrease of the unknown metabolites. The TCE/TCA ratio under anoxia was also altered by pyruvate or lactate infusion.     

Effects of trichloroethylene and its metabolites on rodent hepatocyte intercellular communication

Chronic exposure to trichloroethylene (TCE) results in hepatocellular cancer in mice but not rats. The induction of hepatic tumors by TCE appears to be mediated through nongenotoxic or tumor promotion mechanisms. One cellular effect exhibited by a number of nongenotoxic carcinogens and tumor promoters is the inhibition of gap junction mediated intercellular communication. In the present study, the effects of trichloroethylene (TCE) and its metabolites, trichloracetic acid (TCA), trichloroethanol (TCEth), and chloral hydrate (CH) on gap junction mediated intercellular communication in cultured B6C3F1 mouse and F344 rat hepatocytes were assessed. TCE and TCA inhibited intercellular communication in mouse hepatocytes but not in rat hepatocytes. TCEth and CH had no effect on hepatocyte intercellular communication in either rat or mouse cells. TCE and TCA inhibited intercellular communication in both 24-hr-old and freshly plated mouse hepatocytes. Both compounds produced greater inhibition of intercellular communication in freshly plated cells when compared to 24-hr-old cultures. TCE appeared to require cytochrome P450 metabolism by the mouse hepatocytes to exhibit its inhibitory effect on dye coupling since treatment with SKF-525A prevented the inhibition of intercellular communication by TCE. The inhibitory effect of TCA on intercellular communication was unaffected by treatment with SKF-525A. While the species dependent effect of TCE on intercellular communication may be correlated with different rates and extent of metabolism of TCE by rat and mouse hepatocytes, the inhibiting effect of TCA only on mouse hepatocytes suggests that other intrinsic factors in the male mouse make this species more susceptible to the effects of TCE and TCA on gap junction mediated intercellular communication. These findings may account, in part, for the observed species difference in susceptibility to TCE induced liver carcinogenesis.     

EFFECT OF ETHANOL ON THE METABOLISM OF TRICHLOROETHYLENE IN THE PERFUSED RAT LIVER

The effect of 2 m M ethanol, a concentration indicative of daily alcohol consumption, was investigated on trichloroethylene (TRI) metabolism in perfused Wistar rat liver. The study consisted of two parts: The first part studied TRI administration with or without ethanol. In the second study chloral hydrate (CH), an intermediate in TRI metabolism, was administered in the absence or presence of ethanol to phenobarbital (PB) treated or non-PB-treated rats. The concentrations of the metabolites, total trichloroethanol (TCE), and trichloroacetic acid (TCA) were measured by gas chromatography and intracellular reduced pyridine nucleotides by surface fluorometry. In the first study, ethanol infusion significantly increased the TCE/TCA ratio, TCE production rate, and percentage of reduced pyridine nucleotides, and decreased TCA production rate without an associated change in the sum of TCE and TCA formation rates. In the second study, ethanol infusion in the absence or presence of PB produced similar significant increases in the TCE/TCA ratio, TCE production rate, and percentage of reduced pyridine nucleotides, accompanied by a decrease in TCA formation. The observed shift in TRI metabolism in the presence of ethanol, from oxidation to TCA to reduction to TCE, suggests that alcohol exerts alterations in hepatic intracellular oxidation-reduction (redox) states.     

Metabolism of trichloroethylene in man

Trichloroethylene (Tri) metabolites, i.e. chloral hydrate (Chl), trichloroethanol (TCE) and trichloroacetic acid (TCA), were administered to volunteers to determine the pharmacokinetic activity in the blood and urine. Immediate oxidation of Chl to TCA amounting to approx. 50% was followed by slow subsequent formation of TCA persisting for 30 h. TCA was also formed from TCE over a prolonged interval. After incorporation of Tri, Chl, or TCE, identical half-lives were found for TCE (approx. 12 h), while the TCA half-lives differed greatly, being most prolonged after Tri (approx. 100 h), somewhat lowered after Chl and TCE (approx. 65 h), and shortest after TCA (50 h). The reported findings indicate storage of both Tri and TCE in the tissues from which they are slowly released. As metabolite recovery invariably accounts for less than 50% of the doses ingested, it is suggested that additional pathways of elimination must be operative, chloroform constituting only a minor portion.During industrial operations the degree of Tri inhalation varies considerably from one hour to the next and from day to day. Due to the completely different pharmacokinetic behavior of TCE and TCA, it is not permissible to evaluate previous exposure to Tri on the basis of the urinary TCE and/or TCA excretion.This study was supported by the Deutsche Forschungsgemeinschaft.     

Bayesian population analysis of a harmonized physiologically based pharmacokinetic model of trichloroethylene and its metabolites

Bayesian population analysis of a harmonized physiologically based pharmacokinetic (PBPK) model for trichloroethylene (TCE) and its metabolites was performed. In the Bayesian framework, prior information about the PBPK model parameters is updated using experimental kinetic data to obtain posterior parameter estimates. Experimental kinetic data measured in mice, rats, and humans were available for this analysis, and the resulting posterior model predictions were in better agreement with the kinetic data than prior model predictions. Uncertainty in the prediction of the kinetics of TCE, trichloroacetic acid (TCA), and trichloroethanol (TCOH) was reduced, while the kinetics of other key metabolites dichloroacetic acid (DCA), chloral hydrate (CHL), and dichlorovinyl mercaptan (DCVSH) remain relatively uncertain due to sparse kinetic data for use in this analysis. To help focus future research to further reduce uncertainty in model predictions, a sensitivity analysis was conducted to help identify the parameters that have the greatest impact on various internal dose metric predictions. For application to a risk assessment for TCE, the model provides accurate estimates of TCE, TCA, and TCOH kinetics. This analysis provides an important step toward estimating uncertainty of dose-response relationships in noncancer and cancer risk assessment, improving the extrapolation of toxic TCE doses from experimental animals to humans.     

Alteration of chloral hydrate metabolism in rats with carbon tetrachloride-induced liver damage

The metabolism of chloral hydrate (CH) was investigated in the isolated perfused rat liver system. The experiments were performed on rats that were administered carbon tetrachloride (CCl4) subcutaneously for 15 weeks to induce chronic liver damage and on untreated rats. Clearance of CH from the perfusion system was lower in damaged liver than in control liver. In both groups, 50-70% of the added CH was excreted into perfusate as trichloroethanol (TCE) and trichloroacetic acid (TCA) within 120 min. The TCE/TCA ratio was 1:1.3 in the control group compared to 2:1 in the damaged liver group. The findings suggest that CH metabolism in the liver is affected by chronic damage.     

Metabolism of trichloroethylene in man

Groups of 5 to 6 volunteers each participated in three experimental series involving inhalation of analytically controlled trichloroethylene concentrations for 6 h daily on 5 successive week days: (a) 50 ppm constant, (b) 250 ppm for 12min/h (high peak concentrations, average 50 ppm); (c) 100 ppm constant. The trichloroethanol (TCE) levels in the blood were determined 3 times daily, the TCE and trichloroacetic acid (TCA) levels in the urine twice daily by means of gas Chromatographic (TCE) and colorimetric (TCA) techniques. It was seen that TCE accumulates in the blood from day to day reaching maximum values of (a) 2.0 g/ml, (b) 2.5 g/ml, or (c) 5.0 g/ml; the half life of TCE in the blood was 12 h in each case. After a single dose of 15 mg/kg chloral hydrate (normal hypnotic dose) TCE reached levels of approx. 7 g/ml within 1 h; the pattern of elimination was identical to that obtained after Tri inhalation. The maximum TCE value after 100 ppm Tri coincides with that obtained 2 to 2 1/2 h after ingestion of chloral hydrate. There are some data in the literature indicating that such TCE levels reduce the performance ability in vigilance tests. The formation and accumulation of TCE probably is responsible for the psycho-organic syndrome encountered during occupational exposure to Tri.On inhalation of Tri for several days the urinary excretion of TCE and TCA does not follow certain rules which may be derived from single experiments (for instance, 6 h-inhalations). It would appear, therefore, that the procedures described in the literature for assessment of Tri exposure on the basis of TCE and/or TCA excretion are subject to revision.The described study was supported by the Deutsche Forschungsgemeinschaft.     

Effect of enterohepatic circulation on the pharmacokinetics of chloral hydrate and its metabolites in F344 rats.

Chloral hydrate (CH) is a commonly found disinfection by-product in water purification, a metabolite of trichloroethylene, and a sedative/hypnotic drug. CH and two of its reported metabolites, trichloroacetic acid (TCA) and dichloroacetic acid (DCA), are hepatocarcinogenic in mice. Another metabolite of CH, trichloroethanol (TCE), is also metabolized into TCA, and the enterohepatic circulation (EHC) of TCE maintains a pool of metabolite for the eventual production of TCA. To gain insight on the effects of EHC on the kinetics of CH and on the formation of TCA and DCA, dual cannulated F344 rats were infused with 12, 48, or 192 mg/kg of CH and the blood, bile, urine, and feces were collected over a 48-h period. CH was cleared rapidly (>3000 ml/h/kg) and displayed biphasic elimination kinetics, with the first phase being elimination of the dose and the second phase exhibiting formation rate-limited kinetics relative to its TCE metabolite. The effects of EHC on metabolite kinetics were only significant at the highest dose, resulting in a 44% and 17% decrease in the area under the curve (AUC) of TCA and TCE, respectively. The renal clearance of CH, free TCE (f-TCE), and TCA of 2, 2.7, and 38 ml/h/kg, respectively, indicates an efficient reabsorption mechanism for all of these small chlorinated compounds. DCA was detected at only trace levels (<2 microM) as a metabolite of CH, TCA, or TCE.     

Subchronic toxicity of chloral hydrate on rats: a drinking water study

The subchronic toxicity of chloral hydrate, a disinfection byproduct, was studied in rats following 13 weeks of drinking water exposure. Male (262 +/- 10 g) and female (190 +/- 8 g) Sprague-Dawley rats, ten animals per group, were administered chloral hydrate via drinking water at 0.2, 2, 20 and 200 ppm. Control animals received distilled water only. Gross and microscopic examinations, serum chemistry, hematology, biochemical analysis, neurogenic amine analysis and serum trichloroacetic acid (TCA) analysis were performed at the end of the treatment period. Bronchoalveolar fluids were collected at necropsy and urine specimens were collected at weeks 2, 6 and 12 for biochemical analysis. No treatment-related changes in food and water intakes or body weight gains were observed. There were no significant changes in the weights of major organs. Except for a mild degree of vacuolation within the myelin sheath of the optic nerves in the highest dose males, there were no notable histological changes in the tissues examined. Statistically significant treatment-related effects were biochemical in nature, with the most pronounced being increased liver catalase activity in male rats starting at 2 ppm. Liver aldehyde dehydrogenase (ALDH) was significantly depressed, whereas liver aniline hydroxylase activity was significantly elevated in both males and females receiving the highest dose. A dose-related increase in serum TCA was detected in both males and females starting at 2 ppm. An in vitro study of liver ALDH confirmed that chloral hydrate was a potent inhibitor, with an IC(50) of 8 micro M, whereas TCA was weakly inhibitory and trichloroethanol was without effect. Analysis of brain biogenic amines was conducted on a limited number (n = 5) of male rats in the control and high dose groups, and no significant treatment-related changes were detected. Taking into account the effect on the myelin sheath of male rats and the effects on liver ALDH and aniline hydroxylase of both males and females at the highest dose level, the no-observed-effect level (NOEL) was determined to be 20 ppm or 1.89 mg kg(-1) day(-1) in males and 2.53 mg kg(-1) day(-1) in females. This NOEL is ca. 1000-fold higher than the highest concentration of chloral hydrate reported in the municipal water supply.     

Venous blood levels of inhaled trichloroethylene in female rats and changes induced by interacting agents

The concentration from inhalation of trichloroethylene (TCE) in venous blood from female rats was studied. Exposure consisted of 200, 400 and 500 ppm for 6 hrs, or 50 and 100 ppm for 2 hrs. In each experiment, 1 rat was exposed at a constant concentration of TCE. Blood samples were obtained from an indwelling jugular cannula throughout the experiment. Combination effects with chloral hydrate (0.2 g/kg), ethanol (0.8 ml/kg), isopropanol (0.8 ml/kg), pyrazole (0.2 g/kg), tetraethylthiuram disulfide (TETD; 0.2 g/kg) or tetrachloroethylene (TTCE; 1 g/kg) given orally were observed. The experimental data on the uptake of TCE in blood were fitted, by use of nonlinear regression analysis, to a simple toxicokinetic model. TETD caused the greatest increase in the steady state concentration of TCE (3.7 X), compared to TCE alone at 200 ppm. Isopropanol, pyrazole and TTCE also produced pronounced effects, but chloral hydrate treatment resulted in no significant change. At 50 and 100 ppm TCE exposure for 2 hrs, a significant increase (almost 3 X) in the steady state concentration of TCE from both ethanol and isopropanol was observed.     

Extrahepatic metabolism of chloral hydrate, trichloroethanol and trichloroacetic acid in dogs

To examine the details concerning that part of TRI metabolism which was carried out by the extrahepatic organs, we studied the extrahepatic metabolism of chloral hydrate (CH), free-trichloroethanol (F-TCE) and trichloroacetic acid (TCA) using a method developed in our laboratory. Bypass and non-bypass dogs were given CH, F-TCE and TCA, and we compared the concentrations these substances and their metabolites in the serum and urine of the two groups of animals. In the bypass dogs, F-TCE, TCA and conjugated-trichloroethanol (Conj-TCE) appeared in the blood and urine 30 min. after the CH administration, and TCA and Conj-TCE appeared 30 min. after the F-TCE. All levels of administered substance were higher in bypass dogs than in non-bypass dogs, and the compounds were metabolized in small amounts in the extrahepatic organs compared with the liver. Therefore, administered substances remained at high levels in the serum and were excreted in large amounts in the urine in the form of unchanged substances. The metabolized percentage volumes of CH to TCA in the bypass dogs were 10-20%, and those of F-TCE to TCA were very small, while these percentage values of CH to F-TCE were the same or slightly smaller, respectively. Moreover, trichloroethylene (TRI) acts to decrease the leukocyte count in the blood, but the TRI metabolites described above do not have this function.     

Determination of chloral hydrate metabolites in human plasma by gas chromatography-mass spectrometry

Chloral hydrate (CH) is a widely used sedative. Its pharmacological and toxicological effects are directly related to its metabolism. Prior investigations of CH metabolism have been limited by the lack of analytical techniques sufficiently sensitive to identify and quantify metabolites of CH in biological fluids. In this study a gas chromatography mass spectrometry (GC/MS) method was developed and validated for determining CH and its metabolites, monochloroacetate (MCA), dichloroacetate (DCA), trichloroacetate (TCA) and total trichloroethanol (free and glucuronidated form, TCE and TCE-Glu) in human plasma. Of these, DCA and MCA are newly identified metabolites in humans. The drug, its plasma metabolites and an internal standard, 4-chlorobutyric acid (CBA), were derivatized to their methyl esters by reacting with 12% boron trifluoride-methanol complex (12% BF3-MeOH). The reaction mixture was extracted with methylene chloride and analyzed by GC/MS, using a selected ion monitoring (SIM) mode. The quantitation limits of MCA, DCA, TCA, and TCE were between 0.12 and 7.83 microM. The coefficients of variation were between 0.58 and 14.58% and the bias values ranged between -10.03 and 14.37%. The coefficients of linear regression were between 0.9970 and 0.9996.     

Alteration of the enzymology of chloral hydrate reduction in the presence of ethanol.

The enzymology of chloral hydrate reduction to trichloroethanol was studied in rat liver slices and homogenates. Two enzymes capable of reducing chloral hydrate are present in rat liver and by their properties were found to be aldehyde reductase and alcohol dehydrogenase. The alcohol dehydrogenase catalyzed reaction was very sensitive to the NAD/NADH ratio of the incubation medium and was found to be virtually incapable of performing the reduction with a simulated in vivo coenzyme ratio. The aldehyde reductase catalyzed reaction was relatively insensitive to the NADP/NADPH ratio. Hence, only one of the two possible enzyme systems appears to catalyze the reduction in vivo. Incubations performed with liver slices in the presence or absence of inhibitors and alternative substrates for the two enzyme systems indicated that in the absence of ethanol only aldehyde reductase catalyzed the reduction of chloral hydrate. About a 1.5-fold increase in the rate of reduction of chloral hydrate was observed when 40 mM ethanol was added to the liver slice incubation. Further, deuterium was incorporated into trichloroethanol when the incubations were performed with deuteroethanol. The increased rate of reduction and the deuterium incorporation were both prevented by the inclusion of alcohol dehydrogenase inhibitors (pyrazole and isobutyramide). Thus, in the presence of ethanol, both alcohol dehydrogenase and aldehyde reductase contribute to the reduction of chloral hydrate. Alcohol dehydrogenase is capable of reducing chloral hydrate in the presence of an oxidizable alcohol because it is converted into an enzyme—NADH complex which can then reduce the compound.     

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 0.3–3 mM CH for 3 days or 0.03–3 mM 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 3 mM/day for 3 days. With HRPTC, one sample showed no cytotoxicity to CH at concentrations up to 3 mM/day for 10 days, while in another cytotoxicity was seen at 1 mM/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.     

Identification of trichloroethylene and its metabolites in human seminal fluid of workers exposed to trichloroethylene.

We have investigated the potential of the male reproductive tract to accumulate trichloroethylene (TCE) and its metabolites, including chloral, trichloroethanol (TCOH), trichloroacetic acid (TCA), and dichloroacetic acid (DCA). Human seminal fluid and urine samples from eight mechanics diagnosed with clinical infertility and exposed to TCE occupationally were analyzed. In in vivo experimental studies, TCE and its metabolites were determined in epididymis and testis of mice exposed to TCE (1000 ppm) by inhalation for 1 to 4 weeks. In other studies, incubations of monkey epididymal microsomes were performed in the presence of TCE and NADPH. Our results showed that seminal fluid from all eight subjects contained TCE, chloral, and TCOH. DCA was present in samples from two subjects, and only one contained TCA. TCA and/or TCOH were also identified in urine samples from only two subjects. TCE, chloral, and TCOH were detected in murine epididymis after inhalation exposure with TCE for 1 to 4 weeks. Levels of TCE and chloral were similar throughout the entire exposure period. TCOH levels were similar at 1 and 2 weeks but increased significantly after 4 weeks of TCE exposure. Chloral was identified in microsomal incubations with TCE in monkey epididymis. CYP2E1, a P450 that metabolizes TCE, was localized in human and monkey epididymal epithelium and testicular Leydig cells. These results indicated that TCE is metabolized in the reproductive tract of the mouse and monkey. Furthermore, TCE and its metabolites accumulated in seminal fluid, and suggested associations between production of TCE metabolites, reproductive toxicity, and impaired fertility.     

Metabolism of trichloroethylene

Trichloroethylene was metabolized to chloral hydrate, trichloroethanol and trichloroacetic acid in vitro. The three metabolites in the incubation mixture were determined by gas-liquid chromatography using an electron capture detector. The kinetics of the individual steps of the metabolism of trichloroethylene were investigated in rat liver subcellular fractions or recombined fractions. The general features of trichloroethylene metabolism in vitro were demonstrated by the conversion of trichloroethyleme to the three metabolites (6 per cent total yield) by the 700 g supernatant fraction of rat liver in 2 hr. Oxidation of trichloroethylene to chloral hydrate occurred only in the microsomal fraction of rat liver, as previously reported by Byington and Leibman [5]. (This step was rate-limiting and was stimulated by both phenobarbital and 3-methylcholanthrene pretreatment.) Reduction of chloral hydrate to trichloroethanol occurred in the cytosol of rat liver. This activity was separated into at least three fractions by a DEAE cellulose column—one of them was NADH-dependent and the others were NADPH-dependent.) The formation of trichloroacetic acid from chloral hydrate required cytosol or mitochondria with NAD.