Dynamic effects of miR-20a-5p on hippocampal ripple energy after status epilepticus in rats

To determine the dynamic effects of miR-20a-5p on hippocampal ripple energy in rats after status epilepticus (SE). A lithium pilocarpine (LiCl-PILO)-induced rat model of status epilepticus (SE) was established, and the rats were divided into the normal control (Control, CTL), epileptic control (PILO), valproic acid (VPA + PILO), miR-20a-5p overexpression lentivirus vector (miR + PILO), sponges blocking lentivirus vector (Sponges + PILO), and scramble sequence negative control (Scramble + PILO) groups (n = 6). Electroencephalograms (EEGs) were used to analyze changes in hippocampal ripple energy before and after SE. Quantitative polymerase chain reaction (q-PCR) analysis showed that miR-20a-5p levels gradually increased after miR-20a-5p overexpression lentivirus vector injection into the lateral ventricle, and the miR-20a-5p levels were significantly higher than that in CTL group on days 7 and 36 (P < 0.001). The miR-20a-5p levels decreased significantly on days 7 and 36 after blocking by sponges lentivirus vector injected into the lateral ventricle (P < 0.001). After injection of PILO, the average ripple energy expression in each group gradually increased, and reached the peak before chloral hydrate injection (compared with 1 day before SE, P < 0.05). The ripple energy in the VPA + PILO and Sponges + PILO groups was significantly lower than that in the PILO group at 60 min and 70 min after PILO injection and before chloral hydrate injection (P < 0.05), and maintained lower until 2 h after chloral hydrate injection in VPA + PILO (P < 0.05). Compared with the VPA + PILO group, the mean ripple energy of the Sponges + PILO group had no difference at all time points (P ≥ 0.05). After SE, ripple distribution of space and energy is closely related to the occurrence of epilepsy. Inhibition of miR20a-5p expression can downregulate ripple oscillation energy during seizure.

Toward better understanding of chloral hydrate stability in water: Kinetics, pathways, and influencing factors

Chloral hydrate (CH) is a disinfection byproduct commonly found in disinfected water, and once formed, CH may undergo several transformation processes in water distribution system. In order to understand its fate and occurrence in water, this study examined several factors that may affect the stability of CH in water, including pH, temperature, initial CH concentration, typical anions, and the presence of free chlorine and monochloramine. The results indicated that CH was a relatively stable compound (half-life ∼7 d for 20 μg/L) in ambient pH (7) and temperature (20 °C) conditions. However, the hydrolysis rate can be greatly facilitated by increasing pH (from 7 to 12) and temperature (from 20 to 60 °C) or decreasing initial CH concentration (from 10 mg/L to 20 μg/L). To quantify the influences of these factors on the CH hydrolysis rate constant (k, 1/h), which spans five orders of magnitude, this study developed a multivariate model that predicts literature and this study's data well (R(2) = 0.90). In contrast, the presence of chloride, nitrate, monochloramine, and free chlorine exhibited no significant impacts on the degradation of CH, while the CH loss in non-buffered waters spiked with sodium hypochlorite was driven by alkaline hydrolysis. In terms of reaction products, CH hydrolysis yielded mostly chloroform and formic acid and a few chloride, which confirmed decarburization as a dominant pathway and dehalogenation as a noticeable coexisting reaction.

Chloral hydrate, through biotransformation to dichloroacetate, inhibits maleylacetoacetate isomerase and tyrosine catabolism in humans

BACKGROUND

Chloral hydrate (CH), a sedative and metabolite of the environmental contaminant trichloroethylene, is metabolized to trichloroacetic acid, trichloroethanol, and possibly dichloroacetate (DCA). DCA is further metabolized by glutathione transferase zeta 1 (GSTZ1), which is identical to maleylacetoacetate isomerase (MAAI), the penultimate enzyme in tyrosine catabolism. DCA inhibits its own metabolism through depletion/inactivation of GSTZ1/MAAI with repeated exposure, resulting in lower plasma clearance of the drug and the accumulation of the urinary biomarker maleylacetone (MA), a metabolite of tyrosine. It is unknown if GSTZ1/MAAI may participate in the metabolism of CH or any of its metabolites and, therefore, affect tyrosine catabolism. Stable isotopes were utilized to determine the biotransformation of CH, the kinetics of its major metabolites, and the influence, if any, of GSTZ1/MAAI.

METHODS

Eight healthy volunteers (ages 21-40 years) received a dose of 1 g of CH (clinical dose) or 1.5 μg/kg (environmental) for five consecutive days. Plasma and urinary samples were analyzed by gas chromatography-mass spectrometry.

RESULTS

Plasma DCA (1.2-2.4 μg/mL), metabolized from CH, was measured on the fifth day of the 1 g/day CH dosage but was undetectable in plasma at environmentally relevant doses. Pharmacokinetic measurements from CH metabolites did not differ between slow and fast GSTZ1 haplotypes. Urinary MA levels increased from undetectable to 0.2-0.7 μg/g creatinine with repeated CH clinical dose exposure. Kinetic modeling of a clinical dose of 25 mg/kg DCA administered after 5 days of 1 g/day CH closely resembled DCA kinetics obtained in previously naïve individuals.

CONCLUSIONS

These data indicate that the amount of DCA produced from clinically relevant doses of CH, although insufficient to alter DCA kinetics, is sufficient to inhibit MAAI and tyrosine catabolism, as evidenced by the accumulation of urinary MA.

Biodegradation and biotransformation of wastewater organics as precursors of disinfection byproducts in water

Laboratory experiments were carried out to investigate wastewater organics as the precursors of disinfection byproducts (DBPs) in drinking water supply. The focus was on the change in wastewater DBP precursors during biological degradation under simulated natural conditions. The wastewater and its treated secondary effluent were characterized for DBP formation potential (DBPFP) and DBP speciation profile, including trihalomethanes, haloacetic acids, chloral hydrate, and nitrogen-containing DBPs. Several model organic compounds, including humic acid, tannic acid, glucose, starch, glycine, and bovine serum albumin (BSA), were used to represent the different types of organic pollutants in wastewater discharge. The results show that the DBPFP of wastewater decreased after biodegradation, but the remaining organic matter had a greater DBPFP yield with chlorine. Different model organics displayed different changes in DBPFP during biodegradation. The DBPFP remained largely unchanged for the glycine solution, decreased greatly for the tannic acid and BSA solutions, and increased nearly 3-fold for the glucose and starch solutions after 10d of biodegradation. Meanwhile, the DBPFP yield increased from 3 for glycine to 51μg DBP mg(-1) C for its degradation residue, and from 1 for glucose and starch to 87 and 38μg DBP mg(-1) C for their organic residues, respectively. Although biodegradation may effectively remove some DBP precursors, biotransformation during the process produces new DBP precursors in the form of soluble microbial products (SMPs). The experimental results reveal that SMPs may be an important source of wastewater-derived DBP precursors in natural waters.

Chronic exposure to a trichloroethylene metabolite in autoimmune-prone MRL+/+ mice promotes immune modulation and alopecia

The industrial solvent trichloroethylene (TCE) is a widespread environmental contaminant known to impact the immune system. In the present study, female MRL+/+ mice were treated for 40 weeks with trichloroacetaldehyde hydrate (TCAH), a metabolite of TCE, in the drinking water. The results were compared with the data from an earlier study in which MRL+/+ mice were exposed to TCAH for 4 weeks. Following a 40-week exposure, the mice developed skin inflammation and dose-dependent alopecia. In addition, TCAH appeared to modulate the CD4(+) T-cell subset by promoting the expression of an activated/effector (i.e., CD62L(lo)) phenotype with an increased capacity to secrete the proinflammatory cytokine interferon-gamma. However, unlike what was observed after only 4 weeks of exposure, TCAH did not significantly attenuate activation-induced cell death (AICD) or the expression of the death receptor FasL in CD4(+) T cells. Some metalloproteinases (MMPs) are thought to play a role in susceptibility to AICD by inducing FasL shedding. Thus, both the 4- and 40-week sera were tested for MMP-7 levels in an attempt to explain the disparate results of TCAH on AICD and FasL expression. Serum MMP-7 levels were significantly higher in mice exposed to TCAH for 4 weeks. In contrast, the serum MMP-7 levels were increased in all the mice by 40 weeks when compared with a nonautoimmune strain. Taken together, a chronic exposure to TCAH promotes alopecia and skin inflammation. The early effects of TCAH on MMP-7 levels may provide a mechanism by which TCAH promotes skin pathology.

Key issues in the modes of action and effects of trichloroethylene metabolites for liver and kidney tumorigenesis

Trichloroethylene (TCE) exposure has been associated with increased risk of liver and kidney cancer in both laboratory animal and epidemiologic studies. The U.S. Environmental Protection Agency 2001 draft TCE risk assessment concluded that it is difficult to determine which TCE metabolites may be responsible for these effects, the key events involved in their modes of action (MOAs) , and the relevance of these MOAs to humans. In this article, which is part of a mini-monograph on key issues in the health risk assessment of TCE, we present a review of recently published scientific literature examining the effects of TCE metabolites in the context of the preceding questions. Studies of the TCE metabolites dichloroacetic acid (DCA) , trichloroacetic acid (TCA) , and chloral hydrate suggest that both DCA and TCA are involved in TCE-induced liver tumorigenesis and that many DCA effects are consistent with conditions that increase the risk of liver cancer in humans. Studies of S-(1,2-dichlorovinyl) -l-cysteine have revealed a number of different possible cell signaling effects that may be related to kidney tumorigenesis at lower concentrations than those leading to cytotoxicity. Recent studies of trichloroethanol exploring an alternative hypothesis for kidney tumorigenesis have failed to establish the formation of formate as a key event for TCE-induced kidney tumors. Overall, although MOAs and key events for TCE-induced liver and kidney tumors have yet to be definitively established, these results support the likelihood that toxicity is due to multiple metabolites through several MOAs, none of which appear to be irrelevant to humans.

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.

[Study on decomposed products of trichlorfon in process of gas chromatographic analysis by mass spectrometry]

The decomposed products of trichlorfon in gas chromatographic analysis were identified by mass spectrometry (MS). After MS interpretation, three decomposed products, trichloroacetaldehyde, dimethyl phosphite and dichlorvos were identified. The effects of gas chromatographic conditions on decomposed products of trichlorfon, e. g. injection temperature, injection mode and oven ramp, were studied. The experiments showed that all of the factors have effects on decomposed products of trichlorfon, however, the injection temperature is the key factor to cause trichlorfon being decomposed. The higher the injection temperature is, the bigger the amount of trichlorfon being decomposed. When the injection temperature was raised from 150 degrees C to 250 degrees C, the remaining trichlorfon fell from 86% to 20%. Therefore, on-cold column injection mode gas chromatography or high performance liquid chromatography was recommended for exact quantification of trace trichlorfon.

Pulmonary bioactivation of trichloroethylene to chloral hydrate: relative contributions of CYP2E1, CYP2F, and CYP2B1

Pulmonary cytotoxicity induced by trichloroethylene (TCE) is associated with cytochrome P450-dependent bioactivation to reactive metabolites. In this investigation, studies were undertaken to test the hypothesis that TCE metabolism to chloral hydrate (CH) is mediated by cytochrome P450 enzymes, including CYP2E1, CYP2F, and CYP2B1. Recombinant rat CYP2E1 catalyzed TCE metabolism to CH with greater affinity than did the recombinant P450 enzymes, rat CYP2F4, mouse CYP2F2, rat CYP2B1, and human CYP2E1. The catalytic efficiencies of recombinant rat CYP2E1 (V(max)/K(m) = 0.79) for generating CH was greater than those of recombinant CYP2F4 (V(max)/K(m) = 0.27), recombinant mouse CYP2F2 (V(max)/K(m) = 0.11), recombinant rat CYP2B1 (V(max)/K(m) = 0.07), or recombinant human CYP2E1 (V(max)/K(m) = 0.02). Decreases in lung microsomal immunoreactive CYP2E1, CYP2F2, and CYP2B1 were manifested at varying time points after TCE treatment. The loss of immunoreactive CYP2F2 occurred before the loss of immunoreactive CYP2E1 and CYP2B1. These protein decreases coincided with marked reduction of lung microsomal p-nitrophenol hydroxylation and pentoxyresorufin O-dealkylation. Rates of CH formation in the microsomal incubations were time-dependent and were incremental from 5 to 45 min. The production of CH was also determined in human lung microsomal incubations. The rates were low and were detected in only three of eight subjects. These results showed that, although CYP2E1, CYP2F, and CYP2B1 are all capable of generating CH, TCE metabolism is mediated with greater affinity by recombinant rat CYP2E1 than by recombinant CYP2F, CYP2B1, or human CYP2E1. Moreover, the rates of CH production were substantially higher in murine than in human lung.

Environmental contaminant and disinfection by-product trichloroacetaldehyde stimulates T cells in vitro

It had been shown previously that MRL+/+ mice exposed to occupationally relevant doses of the environmental contaminant trichloroethylene in their drinking water developed lupus-like symptoms and autoimmune hepatitis in association with activation of Interferon-gamma (IFN-gamma)-producing CD4+ T cells. Since trichloroethylene must be metabolized in order to promote the T-cell activation associated with autoimmunity, the present study was initiated to determine whether the immunoregulatory effects of trichloroethylene could be mimicked by one of its major metabolites, trichloroacetaldehyde (TCAA). At concentrations ranging from 0.04 to 1 mM TCAA co-stimulated proliferation of murine T-helper type 1 (Th1) cells treated with anti-CD3 antibody or antigen in vitro. TCAA at similar concentrations also induced phenotypic alterations commensurate with activation (upregulation of CD28 and downregulation of CD62L) in both cloned memory Th1 cells, as well as naïve CD4+ T cells from MRL+/+ mice. TCAA-induced Th1 cell activation was accompanied by phoshorylation of activating transcription factor 2 (ATF-2) and c-Jun, two components of the activator protein-1 (AP-1) transcription factor. TCAA at higher concentrations was also shown to form a Schiff base on T cells, and inhibition of Schiff base formation suppressed the ability of TCAA to phosphorylate ATF-2. Taken together, these results suggest that TCAA promotes T-cell activation via stimulation of the mitogen-activated protein (MAP) kinase pathway in association with Schiff base formation on T-cell surface proteins. By demonstrating that TCAA can stimulate T-cell function directly, these results may explain how the environmental toxicant trichloroethylene promotes T-cell activation and related autoimmunity in vivo.

US Department of Health and Human Services National Toxicology Program. Toxicology and carcinogenesis study of chloral hydrate (ad libitum and dietary controlled) (CAS no. 302-17-0) in male B6C3F1 mice (gavage study)

[structure: see text] Chloral hydrate is used medically as a sedative or hypnotic and as a rubefacient in topical preparations, and it is often given to children as a sedative during dental and other medical procedures. Chloral hydrate is used as a central nervous system depressant and sedative in veterinary medicine and as a general anesthetic in cattle and horses. It is a byproduct of the chlorination of water and has been detected in plant effluent after the bleaching of softwood pulp. Chloral, the anhydrous form of chloral hydrate, is used as a synthetic intermediate in the production of insecticides and herbicides. Chloral hydrate was nominated for study by the Food and Drug Administration based upon widespread human exposure and its potential hepatotoxicity and the toxicity of related chemicals. A dietary control component was incorporated in response to concerns within the regulatory community relating to increased background neoplasm incidences in rodent strains used for toxicity testing and to the proposed use of dietary restriction to control background neoplasm incidence in rodent cancer studies. Male B6C3F1 mice (ad libitum-fed or dietary-controlled) received chloral hydrate (99% pure) by gavage for 2 years. 2-YEAR STUDY IN MALE MICE: Groups of 120 male mice received chloral hydrate in distilled water by gavage at doses of 0, 25, 50, or 100 mg/kg 5 days per week for 104 to 105 weeks. Each dose group was divided into two dietary groups of 60 mice. The ad libitum-fed mice had free access to feed, and the dietary-controlled mice received feed in measured daily amounts calculated to maintain body weight on a previously computed idealized body weight curve. Twelve mice from each diet and dose group were evaluated at 15 months.

SURVIVAL, FEED CONSUMPTION, AND BODY WEIGHTS

Survival of dosed groups of ad libitum-fed and dietary-controlled mice was similar to that of the corresponding vehicle controls. When compared to the ad libitum-fed groups, dietary control significantly increased survival in the vehicle controls and 25 and 50 mg/kg groups. Mean body weights of all dosed groups were similar to those of the vehicle control groups throughout the study. The dietary-controlled mice were successfully maintained at or near their target idealized body weights. There was less individual variation in body weights in the dietary-controlled groups than in the corresponding ad libitum-fed groups. Feed consumption by 25 and 50 mg/kg ad libitum-fed mice was generally similar to that by the vehicle controls throughout the study. Feed consumption by 100 mg/kg ad libitum-fed mice was slightly less than that by the vehicle controls throughout the study.

HEPATIC ENZYME ANALYSIS

Chloral hydrate did not significantly induce either lauric acid 4-hydroxylase activity or CYP4A immunoreactive protein in any of the dosed groups of ad libitum-fed mice. However, 100 mg/kg did significantly induce both lauric acid 4-hydroxylase activity and CYP4A immunoreactive protein in the dietary-controlled mice. Moreover, the induction response profile of CYP4A was similar to the increase in the incidence of liver neoplasms at 2 years in the dietary-controlled mice with the major effect occurring in the 100 mg/kg group. The serum enzymes alanine aminotransferase, amylase, aspartate aminotransferase, and lactate dehydrogenase were also assayed at 2 years. In the ad libitum-fed groups there was a significant increase in aspartate aminotransferase activity in the 50 mg/kg group. There were no other significant effects in any dosed group, but in general the dietary-controlled groups exhibited lower values than the corresponding ad libitum-fed groups.

ORGAN WEIGHTS AND PATHOLOGY FINDINGS

The heart weight of ad libitum-fed male mice administered 100 mg/kg and the kidney weights of 50 and 100 mg/kg ad libitum-fed mice were significantly less than those of the vehicle controls at 2 years. The liver weights of all dosed groups of ad libitum-fed and dietary-controlled mice were greater than those of the vehicle control groups at 2 years, but the increases were not statistically significant. The incidence of hepatocellular adenoma or carcinoma (combined) in ad libitum-fed mice administered 25 mg/kg was significantly greater than that in the vehicle controls at 2 years. The incidences of hepatocellular carcinoma and of hepatocellular adenoma or carcinoma (combined) occurred with positive trends in dietary-controlled male mice at 2 years, and the incidence of hepatocellular carcinoma in 100 mg/kg dietary-controlled mice was significantly increased.

CONCLUSIONS

Under the conditions used in this 2-year gavage study, there was some evidence of carcinogenic activity of chloral hydrate in male B6C3F1 mice based on increased incidences of hepatocellular adenoma or carcinoma (combined) in ad libitum-fed mice and on increased incidences of hepatocellular carcinoma in dietary-controlled mice. In the dietary-controlled mice, induction of enzymes associated with peroxisome proliferation was observed at higher doses.

Metabolism and toxicity of trichloroethylene in epididymis and testis

The widespread occupational exposure to trichloroethylene (TCE) led us to test the hypothesis that TCE causes toxicity in the male reproductive system. We also investigated mechanisms mediating the potential cytotoxic response. Mice were exposed to TCE (1000 ppm) by inhalation for 6 h/day for 5 days/week for a total of 19 days. Exposure after the first week was interspersed by a "weekend." To estimate internal exposure, we measured the TCE metabolites, trichloroacetic acid (TCA) and trichloroethanol (TCOH), in urine at Days 4, 9, 14, and 19. Urinary excretion of TCOH was significantly higher than TCA; levels of TCOH and TCA significantly increased by the second and third week, respectively. Cytochrome P450 2E1 (CYP2E1), an enzyme involved in TCE metabolism, was localized in the epididymal epithelium and testicular Leydig cells, and was found at higher levels in the former than the latter. Immunoblotting confirmed that CYP2E1 protein was present in greater amounts in epididymis than in testis. p-Nitrophenol hydroxylation, a CYP2E1 catalytic activity, was also higher in the epididymis than in the testis. Chloral, a major TCE metabolite, was generated in microsomal incubations at significantly higher levels in epididymis than in testis. Antibody inhibition of CYP2E1 reduced chloral formation, which was more pronounced in epididymis than in testis. After 4 weeks of TCE exposure, damage to the epididymis was manifested as sloughing of epithelial cells. These results indicated that TCE is metabolized in the male reproductive tract, leading to adverse effects that are more severe in the epididymis than in the testis.

Binding of the active metabolite of chloral hydrate, 2,2,2-trichloroethanol, to serum albumin demonstrated using tryptophan fluorescence quenching

Chloral hydrate, a sedative/hypnotic agent widely used in the pediatric population, is converted to the active metabolite 2,2,2-trichloroethanol (TCE) in the liver. Tryptophan fluorescence quenching has been used previously to show that halothane and chloroform bind saturably to serum albumin, and a similar approach is used here to demonstrate that TCE also binds to albumin. TCE quenches the steady-state tryptophan fluorescence of bovine serum albumin (BSA) in a concentration-dependent, saturable manner with a K(D) = 3.3 +/- 0.3 mmol/l. Unlike halothane and chloroform, however, TCE also elicits a concentration-dependent blue-shift in the fluorescence emission spectrum of BSA and human serum albumin. This indicates that TCE induces a conformational change in the protein, causing the tryptophan to experience a change in its chemical environment, thus shifting the peak of the emission spectrum. Circular dichroism spectroscopy revealed a decrease in the alpha-helical content of BSA from 65.8 +/- 0.4 to 62.9 +/- 0.6% when TCE was present at a concentration of 30 mmol/l, providing further evidence for a conformational change. There is evidence that TCE potentiates the action of ligand-gated ion channels such as the GABA(A) and 5-HT(3) receptors, and the present results suggest that anesthetic alcohols may act by binding to these proteins and inducing structural changes that may in turn alter protein function.

Cytochrome p450-dependent metabolism of trichloroethylene in rat kidney

The metabolism of trichloroethylene (Tri) by cytochrome P450 (P450) was studied in microsomes from liver and kidney homogenates and from isolated renal proximal tubular (PT) and distal tubular (DT) cells from male Fischer 344 rats. Chloral hydrate (CH) was the only metabolite consistently detected and was used as a measurement of P450-dependent metabolism of Tri. Pretreatment of rats with pyridine increased CH formation in both liver and kidney microsomes, whereas pretreatment of rats with clofibrate increased CH formation only in kidney microsomes. Pyridine increased CYP2E1 expression in both liver and kidney microsomes, whereas clofibrate had no effect on hepatic but increased renal CYP2E1 and CYP2C11 protein levels. These results suggest a role for CYP2E1 in both the hepatic and renal metabolism of Tri and a role for CYP2C11 in the renal metabolism of Tri. Studies with the general P450 inhibitor SKF-525A and the CYP2E1 competitive substrate chlorzoxazone provided additional support for the role of CYP2E1 in both tissues. CH formation was higher in PT cells than in DT cells and was time and reduced nicotinamide adenine dinucleotide phosphate (NADPH) dependent. However, pretreatment of rats with either pyridine or clofibrate had no effect on CYP2E1 or CYP2C11 protein levels or on CH formation in isolated cells. These data show for the first time that Tri can be metabolized to at least one of its P450 metabolites in the kidneys and quantitate the effect of P450 induction on Tri metabolism in the rat kidney.

Metabolism and toxicity of trichloroethylene and S-(1,2-dichlorovinyl)-L-cysteine in freshly isolated human proximal tubular cells

Trichloroethylene (Tri) caused modest cytotoxicity in freshly isolated human proximal tubular (hPT) cells, as assessed by significant decreases in lactate dehydrogenase (LDH) activity after 1 h of exposure to 500 microM Tri. Oxidative metabolism of Tri by cytochrome P-450 to form chloral hydrate (CH) was only detectable in kidney microsomes from one patient out of four tested and was not detected in hPT cells. In contrast, GSH conjugation of Tri was detected in cells from every patient tested. The kinetics of Tri metabolism to its GSH conjugate S-(1,2-dichlorovinyl)glutathione (DCVG) followed biphasic kinetics, with apparent Km and Vmax values of 0.51 and 24.9 mM and 0.10 and 1.0 nmol/min per mg protein, respectively. S-(1,2-dichlorovinyl)-L-cysteine (DCVC), the cysteine conjugate metabolite of Tri that is considered the penultimate nephrotoxic species, caused both time- and concentration-dependent increases in LDH release in freshly isolated hPT cells. Preincubation of hPT cells with 0.1 mM aminooxyacetic acid did not protect hPT cells from DCVC-induced cellular injury, suggesting that another enzyme besides the cysteine conjugate beta-lyase may be important in DCVC bioactivation. This study is the first to measure the cytotoxicity and metabolism of Tri and DCVC in freshly isolated cells from the human kidney. These data indicate that the pathway involved in the cytotoxicity and metabolism of Tri in hPT cells is the GSH conjugation pathway and that the cytochrome P-450-dependent pathway has little direct role in renal Tri metabolism in humans.

NTP technical report on the toxicity and metabolism studies of chloral hydrate (CAS No. 302-17-0). Administered by gavage to F344/N rats and B6C3F1 mice

Chloral hydrate is widely used as a sedative and a hypnotic in pediatric medicine. It is also a byproduct of water chlorination. Chloral hydrate has been shown to be genotoxic in numerous prokaryotic and eukaryotic assay systems including human lymphocytes in vitro. One of its metabolites, trichloroacetic acid, has demonstrated hepatocarcinogenic activity in mice. Trichloroethylene and perchloroethylene, both of which are metabolized to chloral hydrate, have been shown to be carcinogenic in rats and/or mice. Because of this evidence of carcinogenicity and because of the wide-spread use of chloral hydrate, 16- or 17-day range-finding toxicity studies and separate 16- or 17-day metabolism studies were performed in F344/N rats and B6C3F1 mice in preparation for further long-term rodent studies. In addition, in vitro studies of the metabolism and DNA-binding capacity of chloral hydrate and its metabolites were performed. Genetic toxicity studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, Drosophila melanogaster, and mouse bone marrow cells. For the range-finding studies, groups of eight male and eight female F344/N Nctr BR rats and B6C3F1/Nctr BR (C57BL/6N x C3H/HeN MTV-) mice were administered 0, 50, 100, 200, 400, or 800 mg chloral hydrate per kg body weight in water by gavage 5 days per week for 17 days (rats) or 16 days (mice) for a total of 12 doses. One male rat receiving 800 mg/kg died after five doses. Two 800 mg/kg female rats died after dosing ended but before study termination. One male mouse in each group except the 400 mg/kg group died before the end of the study. Two 800 mg/kg female mice also died before the end of the study. The final mean body weight of 800 mg/kg male rats and the mean body weight gains of 400 and 800 mg/kg males were significantly less than those of the vehicle controls. The mean body weight gains of all groups of dosed male mice were significantly greater than that of the vehicle control group. The only clinical finding in rats and mice attributed to chloral hydrate treatment was light sedation in the 400 mg/kg groups and heavy sedation in the 800 mg/kg groups; sedation subsided within 30 minutes or 3 hours, respectively. The liver weights of 400 mg/kg male mice and 800 mg/kg male and female mice were significantly greater than those of the vehicle control groups. No chemical-related lesions were observed in rats or mice. Male and female rats and mice were administered a single dose of 50 or 200 mg chloral hydrate per kg body weight in water by gavage, or 12 doses of 50 or 200 mg/kg over 17 days (rats) or 16 days (mice). Plasma concentrations of chloral hydrate and its metabolites were determined 15 minutes, 1, 3, 6, and 24 hours, and 2, 4, 8, and 16 days after receiving 1 or 12 doses. Maximum concentrations of chloral hydrate were observed at the initial sampling point of 15 minutes. By 1 hour, the concentrations had dropped substantially, and by 3 hours, chloral hydrate could not be detected in rats or mice. Trichloroacetic acid was the major metabolite detected in the plasma. In rats, the concentrations rose slowly, with the peaks occurring between 1 and 6 hours after treatment. In mice, the peak concentrations were found 1 hour after dosing. The concentrations then slowly decreased such that by 2 days the metabolite could no longer be detected in rats or mice. Trichloroethanol was assayed both as the free alcohol and its glucuronide. In rats, the maximum concentrations of free trichloroethanol occurred at 15 minutes, while the peak concentrations of trichloroethanol glucuronide were found at 1 hour; by 3 hours, concentrations of both metabolites approached background levels. In mice, the maximum concentrations of both metabolites occurred at 15 minutes, and by 1 to 3 hours concentrations approached background levels. The plasma concentrations of chloral hydrate and its metabolites were dose dependent in rats and mice. In mice, plasma concentrations of trichloroacetic acid were significantly higher after a single dose than after 12 doses. None of the metabolic parameters appears to account for species differences that may exist in hepatocarcinogenicity. The data from the study of metabolism and DNA adduct formation indicated that in vitro metabolism of 200 microM to 5 mM chloral hydrate by male B6C3F1 mouse liver microsomes (control microsomes) generated free radical intermediates that resulted in endogenous lipid peroxidation, forming malondialdehyde, formaldehyde, acetaldehyde, acetone, and propionaldehyde. Similar concentrations of trichloroacetic acid and trichloroethanol, the primary metabolites of chloral hydrate, also generated free radicals and induced lipid peroxidation. Lipid peroxidation induced by trichloroacetic acid nearly equaled that induced by chloral hydrate, while that from trichloroethanol was three- to fourfold less. Metabolism of 200 microM to 5 mM chloral hydrate, trichloroacetic acid, and trichloroethanol by liver microsomes of B6C3F1 mice pretreated with pyrazole (pyrazole-induced microsomes) yielded lipid peroxidation products at concentrations two- to threefold greater than those from liver microsomes of untreated mice. Additionally, chloral hydrate-induced lipid peroxidation catalyzed by control and pyrazole-induced microsomes was reduced significantly by 2,4-dichloro-6-phenylphenoxyethylamine, a general cytochrome P450 inhibitor. Human lymphoblastoid transgenic cells expressing cytochrome P(450)2E1 metabolized 200 to 5,000 micrograms/mL chloral hydrate to reactants inducing mutations, whereas the parental cell line was inactive. The malondialdehyde-modified DNA adduct, 3-(2-deoxy-beta-D-erythro-pentofuranosyl)pyrimido[1,2 alpha]purin-10(3H)-one (MDA-MG-1), formed from the metabolism of 1 mM chloral hydrate, trichloroacetic acid, and trichloroethanol by control B6C3F1 mouse liver microsomes, mouse pyrazole-induced microsomes, male F344/N rat liver microsomes, and human liver microsomes in the presence and absence of calf thymus DNA was also determined. When incubated in the absence of calf thymus DNA, the amount of malondialdehyde formed from metabolism by pyrazole-induced mouse microsomes was twice that from rat or human liver microsomes. Amounts of chloral hydrate-induced and trichloroacetic acid-induced lipid peroxidation products formed from metabolism by rat and human liver microsomes were similar, and these quantities were about twice those formed from the metabolism of trichloroethanol. The quantity of MDA-MG-1 formed from the metabolism of chloral hydrate, trichloroacetic acid, and trichloroethanol by mouse, rat, and human liver microsomes exhibited a linear correlation with the quantity of malondialdehyde formed under incubation conditions in the absence of calf thymus DNA. Chloral hydrate was shown to be mutagenic in vitro and in vivo. At doses from 1,000 to 10,000 micrograms/plate, it induced mutations in S. typhimurium strain TA100, with and without S9 activation; an equivocal response was obtained in S. typhimurium strain TA98 in the absence of S9, and no mutagenicity was detected with strain TA1535 or TA1537. Chloral hydrate at doses from 1,700 to 5,000 micrograms/mL induced sister chromatid exchanges; at doses from 1,000 to 3,000 micrograms/mL, chromosomal aberrations were induced in cultured Chinese hamster ovary cells, with and without S9. Results of a sex-linked recessive lethal test in D. melanogaster were unclear; administration of chloral hydrate by feeding produced an inconclusive increase in recessive lethal mutations, results of the injection experiment were negative. An in vivo mouse bone marrow micronucleus test with chloral hydrate at doses from 125 to 500 mg/kg gave a positive dose trend. In summary, due to the absence of chloral hydrate-induced histopathologic lesions in rats and mice, no-observed-adverse-effect levels (NOAELs) were based on body weights of rats and liver weights of mice. The NOAELs for rats and mice were 200 mg/kg. Chloral hydrate was rapidly metabolized by rats and mice, with trichloroacetic acid occurring as the major metabolite. Peak concentrations of trichloroacetic acid occurred more quickly in mice. Plasma concentrations of chloral hydrate were dose dependent, but metabolic rates were unaffected by dose or sex. Chloral hydrate was mutagenic in vitro and in vivo. Metabolism of chloral hydrate and its metabolites produced free radicals that resulted in lipid peroxidation in liver microsomes of mice, rats, and humans. Induction of cytochrome P(450)2E1 by pyrazole increased the concentrations of lipid peroxidation products; inhibition of cytochrome P(450)2E1 by 2,4-dinitrophenylhydrazine reduced these concentrations. Metabolism of chloral hydrate and its metabolites by mouse, rat, and human liver microsomes formed malondialdehyde, and in the presence of calf thymus DNA formed the DNA adduct MDA-MG-1.

Physiologically based pharmacokinetic modeling of inhaled trichloroethylene and its oxidative metabolites in B6C3F1 mice

A physiologically based pharmacokinetic (PBPK) model for inhaled trichloroethylene (TCE) was developed for B6C3F1 mice. Submodels described four P450-mediated metabolites of TCE, which included chloral hydrate (CH), free and glucuronide-bound trichloroethanol (TCOH-f and TCOH-b), trichloroacetic acid (TCA), and dichloroacetic acid (DCA). Inhalation time course studies were carried out for calibration of the model by exposing mice to TCE vapor concentrations of either 100 or 600 ppm for 4 h. At several time points, mice were euthanized and blood, liver, kidney, lung, and fat were collected and analyzed for TCE and its oxidative metabolites. Peak blood TCE concentrations were 0.86 and 7.32 microgram/mL, respectively, in mice exposed to 100 and 600 ppm TCE. The model overpredicted the mixed venous blood and tissue concentrations of TCE for mice of both exposure groups. Fractional absorption of inhaled TCE was proposed to explain the discrepancy between the model predictions and the TCE blood time course data. When fractional absorption (53%) of inhaled TCE was incorporated into the model, a comprehensive description of the uptake, distribution, and clearance of TCE in the blood was obtained. Fractional uptake of inhaled TCE was further verified by collecting TCE in exhaled breath following a 4-h constant concentration exposure to TCE and validation was provided by testing the model against TCE blood concentrations from an independent data set. The submodels adequately simulated the distribution and clearance kinetics of CH and TCOH-f in blood and the lungs, TCOH-b in the blood, and TCA and DCA, which were respectively detected for up to 43 and 14 h postexposure in blood and livers of mice exposed to 600 ppm TCE. This is the first extensive tissue time course study of the major metabolites of TCE following an inhalation exposure to TCE and the PBPK model predictions were in good general agreement with the observed kinetics of the oxidative metabolites formed in mice exposed to TCE concentrations of 100 and 600 ppm.

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.

Alkyl halides, super hydrogen production and the pathogenesis of pneumatosis cystoides coli

BACKGROUND AND AIMS

The colons of patients with pneumatosis cystoides coli produce excessive H2. Exposure to alkyl halides could explain this. Six consecutive patients who had pneumatosis cystoides coli while taking chloral hydrate (1-5+ g/day) are reported. Patients 2 and 3 were investigated after they had ceased chloral hydrate treatment. One produced methane, the other did not. (Pneumatosis cystoides coli patients are non-methanogenic according to the literature.) Both had overnight fasting breath H2 of less than 10 ppm. A literature review disclosed just one patient who was using chloral at the time of diagnosed pneumatosis cystoides coli, but an epidemic of the disease in workers exposed to trichloroethylene.

METHODS

(i) In vitro experiments with human faeces: chloral or closely related alkyl halides were added to anaerobic faecal cultures derived from four methane-producing and three non-methanogenic human subjects. H2 and CH4 gases were measured. (ii) In vivo animal experiment: chloral hydrate was added to drinking water of four Wistar rats, and faecal H2 compared with control rats.

RESULTS

Alkyl halides increased H2 up to 900 times in methanogenic and 10 times in non-methanogenic faecal cultures. The Ki of chloral was 0.2 mM. Methanogenesis was inhibited in concert with the increase in net H2. In the rat experiment, chloral hydrate increased H2 10 times, but did not cause pneumatosis.

CONCLUSIONS

Chloral and trichloroethylene are alkyl halides chemically similar to chloroform, a potent inhibitor of H2 consumption by methanogens and acetogens. These bacteria are the most important H2-consuming species in the colon. It is postulated that exposure to these alkyl halides increases net H2 production, which sets the scene for "counterperfusion supersaturation" and the formation of gas cysts. In recent times, very low prescribing rates for chloral have caused primary pneumatosis cystoides to become extremely rare. As with primary pneumatosis, secondary pneumatosis cystoides, which occurs if there is small bowel bacterial overgrowth distal to a proximally located gut obstruction, is predicted by counterperfusion supersaturation. "Inherent unsaturation" due to metabolism of O2 is a safety factor, which could explain why gas bubbles do not form more often in tissue with high H2 tension.

A physiologically based pharmacokinetic model for trichloroethylene and its metabolites, chloral hydrate, trichloroacetate, dichloroacetate, trichloroethanol, and trichloroethanol glucuronide in B6C3F1 mice

A six-compartment physiologically based pharmacokinetic (PBPK) model for the B6C3F1 mouse was developed for trichloroethylene (TCE) and was linked with five metabolite submodels consisting of four compartments each. The PBPK model for TCE and the metabolite submodels described oral uptake and metabolism of TCE to chloral hydrate (CH). CH was further metabolized to trichloroethanol (TCOH) and trichloroacetic acid (TCA). TCA was excreted in urine and, to a lesser degree, metabolized to dichloroacetic acid (DCA). DCA was further metabolized. The majority of TCOH was glucuronidated (TCOG) and excreted in the urine and feces. TCOH was also excreted in urine or converted back to CH. Partition coefficient (PC) values for TCE were determined by vial equilibrium, and PC values for nonvolatile metabolites were determined by centrifugation. The largest PC values for TCE were the fat/blood (36.4) and the blood/air (15.9) values. Tissue/blood PC values for the water-soluble metabolites were low, with all PC values under 2.0. Mice were given bolus oral doses of 300, 600, 1200, and 2000 mg/kg TCE dissolved in corn oil. At various time points, mice were sacrificed, and blood, liver, lung, fat, and urine were collected and assayed for TCE and metabolites. The 1200 mg/kg dose group was used to calibrate the PBPK model for TCE and its metabolites. Urinary excretion rate constant values were 0. 06/hr/kg for CH, 1.14/hr/kg for TCOH, 32.8/hr/kg for TCOG, and 1. 55/hr/kg for TCA. A fecal excretion rate constant value for TCOG was 4.61/hr/kg. For oral bolus dosing of TCE with 300, 600, and 2000 mg/kg, model predictions of TCE and several metabolites were in general agreement with observations. This PBPK model for TCE and metabolites is the most comprehensive PBPK model constructed for P450-mediated metabolism of TCE in the B6C3F1 mouse.

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.

Chloral hydrate formation in the Japanese medaka minnow

Trichloroethylene (TRI) is a common groundwater contaminant that has been shown to be tumorigenic and toxic in laboratory animals. The toxicity of TRI is increased by inducing the production of cytochrome P-450-dependent metabolites. Cytochrome P450 (CYP) 2E1 metabolizes TRI in mammals; however, this isoform of CYP2E1 does not appear to be expressed in fish. Medaka microsomal protein containing CYP was exposed to TRI and extracted with ethyl acetate. The extract was analyzed using gas chromatography (liquid injection) with an electron capture detector and separately using mass spectrometry. The formation of chloral hydrate, a precursor of toxic metabolites, was confirmed following exposure of hepatic microsomes of the medaka to TRI. These results indicate that medaka catalyze the first step in the formation of toxic metabolites and CYP forms in addition to CYP2E1 which catalyzes this reaction in fish.

Characterisation of atypical biotype 3, serotype O:3 Yersinia and development of a simple identification scheme

Five clinical strains of Yersinia isolated in Japan and identified as atypical biotype 3 or biotype 3B, serotype O:3, phage type II (3*/O:3/II) Yersinia enterocolitica were characterised since the biochemical reactions of these strains indicate they might also belong to the species Yersinia bercovieri. Biochemical tests, characterisation of the beta-lactamases and DNA-DNA hybridization studies provided strong evidence indicating that these strains should be classified as Yersinia enterocolitica. A simple scheme combining a disc diffusion test and four biochemical tests was devised for identification of these atypical strains.

Pharmacokinetic analysis of chloral hydrate and its metabolism in B6C3F1 mice

Chloral hydrate (CH) and its metabolites, trichloroacetate (TCA) and dichloroacetate (DCA), have been shown to induce liver tumors in male B6C3F1 mice. The pharmacokinetics of CH and its metabolites play an important role in its toxicity. This study was designed to characterize the kinetics of CH metabolism, and the formation and elimination of TCA, DCA, trichloroethanol (TCOH), and trichloroethanol glucuronide (TCOG) in male B6C3F1 mice. Mice were dosed with 67.8, 678, and 2034 micromol/kg of CH through the tail vein. At selected time points, mice were killed, and blood and liver samples were collected. Samples were assayed by GC for CH, TCOH, TCOG, TCA, and DCA concentrations. After intravenous administration, CH rapidly disappeared from blood with a terminal half-life ranging from 5 to 24 min. Systemic clearance decreased from 36.0 to 7.6 liters/kg-hr with increasing CH dose, demonstrating dose-dependent pharmacokinetics. TCOH, TCOG, TCA, and DCA were detected over the study period. Formation and metabolism of CH metabolites seemed to be dose-dependent. The terminal half-lives of TCOH and TCOG were similar, ranging from 0.2 to 0.7 hr. TCA and DCA were formed rapidly from the metabolism of CH and cleared slowly from systemic circulation. The area under the blood concentration-time curve for DCA was 10-20% of that for TCA. Both TCA and DCA were slowly eliminated from systemic circulation. The concentration-time profile of DCA seemed to be driven by the blood concentration of TCA, suggesting the possibility of DCA formation from TCA metabolism.

A species comparison of chloral hydrate metabolism in blood and liver

Chloral hydrate (CH), [302-17-0], is a human sedative useful in premature infants. No current epidemiological study supports increased cancer risk. CH is also a rodent toxicant and a P450-derived metabolite of trichloroethylene (TRI). P450 induction increases TRI toxicity in rodents. CH is very rapidly metabolized to trichloroacetic acid (TCA) and trichloroethanol (TCOH). Because TCA mediates some responses following TRI exposure, we assessed the metabolism of CH to TCA and TCOH by liver and blood of the rat, mouse, and human. Both TCA and TCOH are formed in blood and liver. The constants for hepatic TCA and TCOH formation are presented. The K(m) for hepatic TCOH formation is at least ten-fold lower than for TCA formation in these species. Clearance values for TCOH are higher than for TCA. These data support TCOH as the first major metabolite of TRI and CH in vivo.

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.

Determination of chloral hydrate and metabolites in a fatal intoxication

A young woman (32 years old) was found dead in her house. Screening of postmortem blood with enzyme multiplied immunoassay (EMIT) detected benzodiazepines, salicylic acid derivatives, and caffeine. These compounds were present in nontoxic concentrations as confirmed by thin-layer chromatography and high-performance liquid chromatography. The Fujiwara-Ross reaction on blood revealed the presence of chlorinated hydrocarbons in high concentrations. An optimized gas chromatographic method with electron capture detection allowed the identification and quantitation of chloral hydrate and both its metabolites, 2,2,2-trichloroethanol and trichloroacetic acid, in the available postmortem samples. The tissue concentrations indicated that chloral hydrate ingestion could be identified as the cause of this fatality.

The effect of chloral hydrate and its metabolites, trichloroethanol and trichloroacetic acid, on bilirubin-albumin binding

Chloral hydrate is used as a sedative in infants requiring ventilatory support. The metabolites, trichloroethanol and trichloroacetic acid, accumulate in the serum and are protein bound. The possibility that these chemicals might compete with bilirubin for albumin binding was tested using the peroxidase method and a dialysis rate method. Chloral hydrate and trichloroethanol had no effect on bilirubin-albumin binding. Trichloroacetic acid affects bilirubin-albumin binding but to a degree that would be dangerous only in infants with an unusual accumulation of this metabolite.

Sex-, age- and pregnancy-induced changes in the metabolism of toluene and trichloroethylene in rat liver in relation to the regulation of cytochrome P450IIE1 and P450IIC11 content

Sex-, age- and pregnancy-induced changes in the metabolism of toluene and trichloroethylene in rat liver were investigated in relation to the regulation of cytochrome P450IIE1 and P450IIC11 content using monoclonal antibodies. Immature male rats had a higher level of microsomal protein than females, and this increased with development; however, no difference by sex was found at puberty. No difference in cytochrome P450 content was seen between immature male and female rats; the content increased with development only in males, so that a sex difference in cytochrome P450 content occurred at puberty. Pregnancy decreased the cytochrome P450 content but not that of the microsomal protein. The rate of formation of benzyl alcohol from toluene was 4 times higher in mature than in immature male rats at a high concentration of toluene, but no difference was seen at a low toluene concentration. In contrast, the rate was lower in mature female rats than in immature ones at a low toluene level and no difference was seen at the high concentration. A sex difference was thus found in benzyl alcohol formation at puberty at both concentrations of toluene. The levels of o- and p-cresol formation in liver were similar in males and females but the rate decreased during development of females. The rate of metabolism of trichloroethylene was higher in immature than in mature male and female rats, especially at a low substrate level, and no sex difference in metabolism was seen with either age or concentration of trichloroethylene. Pregnancy decreased the metabolism of both toluene and trichloroethylene.(ABSTRACT TRUNCATED AT 250 WORDS)

A comparative study on the contribution of cytochrome P450 isozymes to metabolism of benzene, toluene and trichloroethylene in rat liver

The contribution of P450IIE1, P450IIC11/6, P450IIB1/2 and P450IA1/2 to the formation of chloral hydrate (CH) from trichloroethylene (TRI) was investigated in microsomes from control, ethanol-, phenobarbital (PB)- and 3-methylcholanthrene (MC)-treated rats using monoclonal antibodies (MAbs) to the respective P450 isozymes, and compared with their roles in benzene and toluene metabolism. Anti-P450IIE1 inhibited the formation of CH from TRI more strongly in microsomes from ethanol-treated rats than in microsomes from control rats at low concentration of TRI when net inhibition was compared. Anti-P450IIC11/6 inhibited CH formation in microsomes from control and PB-treated rats at high, not low, concentration of TRI, but the net inhibition in control microsomes was less than that due to anti-P450IIE1. Anti-P450IIB1/2 and anti-P450IA1/2 also inhibited CH formation from TRI in microsomes from PB- and MC-treated rats, respectively, stronger at high substrate concentration than at low concentration. These results indicate that P450IIE1, P450IIC11/6, P450IIB1/2 and P450IA1/2 are involved in the metabolic step from TRI to CH, and the first isozyme may be a low-Km TRI oxidase and the others high-Km one. Comparing the contributions of four isozymes to benzene, toluene and TRI metabolism, all four acted in the metabolism of these compounds, but P450IIE1 did not catalyse o-cresol formation nor P450IA1/2 benzyl alcohol formation from toluene, suggesting regioselectivity of toluene metabolism in the action of these two isozymes. The contribution of P450IIE1 in benzene and TRI oxidation was greater than that of P450IIC11/6, but the reverse was seen with respect to benzyl alcohol formation from toluene, indicating that P450IIC11/6 is relatively inactive towards benzene and TRI oxidation, but is primarily involved in toluene metabolism. P450IIB1/2 and P450IIC11/6 attacked all the metabolic positions studied, but only in the side-chain metabolism of toluene was their contribution significant, suggesting that these two isozymes are quite similar in function.

Aldehyde dismutation catalyzed by pulmonary carbonyl reductase: kinetic studies of chloral hydrate metabolism to trichloroacetic acid and trichloroethanol

The kinetics of the NAD(P)(+)-linked aldehyde dismutation by pulmonary carbonyl reductase of guinea pig were studied using a highly hydrated substrate, chloral hydrate (CH). The enzyme irreversibly converted the substrate into trichloroacetic acid (TCA) and trichloroethanol (TCE) in the presence of the reduced or oxidized cofactors, of which NAD(P)+ gave a higher reaction rate than did NAD(P)H, and the concentration ratios of the two products (TCA plus TCE) to CH utilized were 1:1. In the NAD(P)(+)-linked reaction TCA was the predominant product and its amount was compatible with that of TCE plus NAD(P)H produced, whereas in the NAD(P)H-linked reaction equal amounts of TCA and TCE were formed and the cofactor was little oxidized. These results suggest that the enzyme oxidized the hydrated aldehydes to TCA with NAD(P)+ as the cofactor and reduced the unhydrated aldehyde to TCE with NAD(P)H. The steady-state kinetic measurements in the NADP(+)-linked CH oxidation were consistent with an ordered Bi Bi mechanism which is the same as that for the secondary alcohol oxidation by the enzyme. The dehydrogenase activity was inhibited competitively with respect to CH by a secondary alcohol substrate, propan-2-ol. The CH and propan-2-ol dehydrogenase activities were similarly inactivated by 2,4,6-trinitrobenzene-sulfonate, and NADP(H), several cofactor analogs and a cofactor-competitive inhibitor, Cibacron blue dye, protected against the inactivation, which suggest that lysine residues are essential for catalysis.

Fate of 2,2,2-trichloroacetaldehyde (chloral hydrate) produced during trichloroethylene oxidation by methanotrophs

Four different methanotrophs expressing soluble methane monooxygenase produced 2,2,2-trichloroacetaldehyde, or chloral hydrate, a controlled substance, during the oxidation of trichloroethylene. Chloral hydrate concentrations decreased in these cultures between 1 h and 24 h of incubation. Chloral hydrate was shown to be biologically transformed to trichloroethanol and trichloroacetic acid by Methylosinus trichosporium OB3b. At elevated pH and temperature, chloral hydrate readily decomposed and chloroform and formic acid were detected as products.

Three forms of trichloroethylene-metabolizing enzymes in rat liver induced by ethanol, phenobarbital, and 3-methylcholanthrene

In vitro metabolism of trichloroethylene (TRI) and trichloroethanol (TCE) was investigated using liver microsomes from control and ethanol-, phenobarbital (PB)-, and 3-methylcholanthrene (MC)-treated rats. At least three forms of enzymes were involved in TRI metabolism. One was a low-Km type normally existing in microsomes from control rats. The ethanol-inducible enzyme was found to be catalytically identical to this low-Km isozyme. Another was a high-Km type which was induced exclusively by PB, and a third was an MC-inducible isozyme with a Km value between those of ethanol- and PB-inducible isozymes. Although MC treatment did not affect the rate of TRI metabolism in vitro, both ethanol and PB treatment markedly enhanced the metabolism. Ethanol-induced enhancement was different from PB-induced enhancement in that ethanol enhanced the metabolism predominantly at low substrate concentrations, whereas PB did so at high concentrations. In addition, TRI metabolism with enzymes from ethanol-treated rats was inhibited by the substrate itself at high concentrations. MC treatment of rats had little or no influence on the rate of TCE metabolism in vitro, whereas both ethanol and PB enhanced the microsomal conversion of TCE to chloral hydrate. As in the case of TRI metabolism, ethanol induced a microsomal TCE-metabolizing enzyme of low Km, whereas PB preferentially induced an enzyme of high Km.

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.

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.

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.

The cholecystohepatic circulation of trichloroethylene and its metabolites in dogs

In order to examine the cholecystohepatic circulation of trichloroethylene (TRI) and its metabolites, we injected the gallbladder with TRI and its metabolites, i.e. chloral hydrate (CH), free-trichloroethanol (F-TCE), trichloroacetic acid (TCA) and conjugated-trichloroethanol (Conj-TCE), using anesthetized dogs. The absorption rates of water from the gallbladder were 25-30% 2 h after administration for all substances. The absorption rates of substances were 65-70% in the CH, F-TCE and TRI groups, and 40-50% in the Conj-TCE and TCA groups 2 h after the administration. Conj-TCE in the blood absorbed from the gallbladder has a tendency to be directly transported to the venous system rather than to be taken into hepatocytes in the liver. All of the administered substances, in particular, F-TCE might be metabolized to other substances in the gallbladder.

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.

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.

Chemical modification of human aldehyde dehydrogenase by physiological substrate

Employing 3,4-dihydroxyphenylacetaldehyde (dopal) as a substrate for human aldehyde dehydrogenase (aldehyde:NAD+ oxidoreductase, EC 1.2.1.3) in anaerobic conditions, inactivation of both cytoplasmic E1 and mitochondrial E2 isozymes during catalysis has been observed. Incorporation of 14C-labelled dopal has been demonstrated by retention of label following denaturation and exhaustive dialysis and by peptide mapping following tryptic digestion. Incorporation of label gave linear plots vs. activity remaining with up to two molecules incorporated per molecule of enzyme and 30% activity remaining. Further incorporation (up to 16 molecules) occurred, but was non-linear when plotted vs. activity remaining. Protection against activity loss during incorporation of the first two molecules was afforded by NAD, NADH, chloral, and by chloral and NAD together, the last being the most effective. Saturation kinetics gave y-axis intercepts, suggesting interaction at a specific point on the enzyme surface. The Ki value from saturation kinetics was the same as that from the slope replot in catalytic reaction. Peptide mapping of tryptic digests showed that a single peptide was labelled, confirming specificity of interaction. Even in the absence of complete inactivation, the results suggest that reaction with the first two molecules occurs at some point on the enzyme surface important for enzyme activity. The possibility of such a reaction occurring in vivo is discussed.

Biliary excretion of trichloroethylene and its metabolites in dogs

To examine the biliary excretion of trichloroethylene (TRI) and its metabolites, we carried out various experiments with TRI and its metabolites, i.e., chloral hydrate (CH), free-trichloroethanol (F-TCE) and trichloroacetic acid (TCA), using anesthetized dogs. The amount of biliary excretion was significantly increased with the administration of CH and F-TCE, whereas it remained at control levels with the administration of TRI and TCA. The substances excreted into bile were conducted in the form of conjugated-TCE (Conj-TCE) in over 90% of the CH, F-TCE and TRI administration groups. About 95% of these Conj-TCE were conjugated with glucuronic acid. The cumulative excretion ratios of substances and metabolites to dose were 20% for CH and F-TCE, and about 1% for TCA and TRI 2 h after administration.

Interactions of paraldehyde with ethanol and chloral hydrate

The interaction of the depressant and toxic actions of paraldehyde with those of ethanol and chloral hydrate were investigated in two strains of male mice by determination of the ED50 for anesthetic action (righting reflex loss) and the 24 hr LD50, respectively. In all instances less than simple additive synergism was observed. Onset and duration times for the anesthetic actions of paraldehyde and ethanol were observed to be almost identical. Investigation of the time of maximum toxic effect revealed paraldehyde itself and mixtures containing 40% or more paraldehyde to be more acutely toxic than ethanol or mixtures containing more than 80% ethanol, suggesting the possibility of different mechanism of toxic action as contributory reasons for the less than simple additivity of the lethal effects of these two agents. The onset and duration of the anesthetic effect of chloral hydrate was longer than that of equipotent doses of paraldehyde, binary mixtures of these two agents having intermediate onset times but much longer duration than either compound, leading to the conclusion the less than simple additivity observed with respect to both the depressant and toxic actions of paraldehyde and chloral hydrate resulted from different time courses of action.

Chloral hydrate: unusually high concentrations in a fatal overdose

A case in which chloral hydrate as a pure chemical rather than the prescribed drug caused the death of a 27-year-old white male is presented. Trichloroethanol was quantified in blood and tissues by electron capture gas chromatography. The blood trichloroethanol concentration found in this case (1700 mg/L) was higher than had been previously reported in the literature.

Enzymatic requirement for cyanamide inactivation of rat liver aldehyde dehydrogenase

The in vitro inactivation of aldehyde dehydrogenase (ALDH) by cyanamide in rat liver slices, in intact mitochondria, and at various stages of purity was characterized. Low-Km ALDH was more susceptible to cyanamide inactivation than was the high-Km form. In addition, the presence of NAD or NADH was necessary for cyanamide inhibition of the ALDH activity. Cyanamide at low concentrations required enzymatic conversion to a reactive derivative that could inhibit ALDH. The data in this study are consistent with the suggestion of DeMaster et al. [Biochem. biophys. Res. Commun., 122, 358 (1984)] that catalase is the cyanamide-converting enzyme. An inhibitor of catalase activity, malonate, decreased the rate of cyanamide inactivation of ALDH in intact mitochondria. Furthermore, affinity chromatography-purified ALDH, free of catalase activity, was not susceptible to cyanamide inactivation. This affinity-purified ALDH was only inactivated by high concentrations of cyanamide. Thus, an alternative pathway for ALDH inactivation may exist in which enzymatic modification of cyanamide is not necessary. It is more likely, however, that a contaminating enzyme in the ALDH preparation is capable of activating cyanamide.

Bovine lens aldehyde dehydrogenase. Kinetics and mechanism

Bovine lens cytoplasmic aldehyde dehydrogenase exhibits Michaelis-Menten kinetics with acetaldehyde, glyceraldehyde 3-phosphate, p-nitrobenzaldehyde, propionaldehyde, glycolaldehyde, glyceraldehyde, phenylacetylaldehyde and succinic semialdehyde as substrates. The enzyme was also active with malondialdehyde, and exhibited an esterase activity. Steady-state kinetic analyses show that the enzyme exhibits a compulsory-ordered ternary-complex mechanism with NAD+ binding before acetaldehyde. The enzyme was inhibited by disulfiram and by p-chloromercuribenzoate, and studies with with mercaptans indicated the involvement of thiol groups in catalysis.

The effect of dietary protein quantity on the activity of UDP-glucuronyltransferase and its physiological significance in drug metabolism

Low dietary protein has been shown to induce the activity of rat hepatic UDP-glucuronyltransferase (UDPGTase) as measured in vitro. The assay of UDPGTase in vitro is hampered by the need to solubilize the microsomal membrane, without destroying the physiological significance of the measurements. The present work was to determine the effect of dietary protein on the activity of UDPGTase and on the activity of UDP-glucose dehydrogenase. Chloral hydrate induced sleeping time was used as a bioassay for UDPGTase, confirming the physiological significance of the in vitro analysis. Sixty male rats were maintained on three different protein levels (7.5, 15, and 45%) for 16 days. Fifteen rats from each group were sacrificed and hepatic UDPGTase, cytochrome P-450, UDP-glucose dehydrogenase, and alcohol dehydrogenase were assayed. Five rats from each group were dosed with 7.5% chloral hydrate (4.8 mL/kg body weight) to measure sleeping time. Rats on 7.5% dietary protein had significantly higher UDPGTase activity than rats fed either 15 or 45% protein diets. These differences in enzyme activity in vitro correlated with the differences in chloral hydrate sleeping time. Dietary protein was not found to affect the activity of UDP-glucose dehydrogenase as measured in vitro.