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Biomedical subjects

G L Kedderis

Publications and source records attributed to G L Kedderis.

At least 37 records · Page 2Linked to original sources

The role of regenerative cell proliferation in chloroform-induced cancer.

Chloroform produces cancer by a nongenotoxic-cytotoxic mode of action, with no increased cancer risk expected at noncytotoxic doses. The default risk assessment for inhaled chloroform relies on liver tumor incidence from a gavage study with female B6C3F1 mice and estimates a virtually safe dose (VSD) at an airborne concentration of 0.000008 ppm of chloroform. In contrast, a 1000-fold safety factor applied to the NOAEL for liver cytotoxicity from inhalation studies yields a VSD of 0.01 ppm. This estimate relies on inhalation data and is more consistent with the mode of action of chloroform.

Animals↗

Determination of tissue partition coefficients for volatile tissue-reactive chemicals: acrylonitrile and its metabolite 2-cyanoethylene oxide.

Partition coefficients (PCs) are chemical-specific parameters used in physiologically based pharmacokinetic models to describe chemical solubility in tissues. Tissue:air PCs for volatile chemicals can be estimated using vial equilibration techniques in which the chemical concentration in the vial headspace is measured by gas chromatography after equilibrium is reached between the chemical in tissue and air. However, equilibrium would not be expected with tissue-reactive chemicals such as acrylonitrile (ACN) or its epoxide metabolite 2-cyanoethylene oxide (CEO). Active uptake of ACN was observed in rat blood due to reaction with blood sulfhydryl groups, while CEO reacted with all tissues examined (rat blood, muscle, fat, liver, and brain). The active uptake processes were first order as evidenced by a linear decrease in the log of the vial headspace concentrations over time. Linear extrapolation of the log of the apparent PC to zero time, where the contribution of the active uptake process is zero, yielded an estimated PC of 487 for ACN in blood. Equilibrium was achieved with ACN after treatment of blood with diethyl maleate to modify blood sulfhydryl groups, with a PC of 512 +/- 29 (mean +/- SE, n = 14). These PC estimates were verified by direct measurement of ACN concentrations in both the air and the blood (stabilized by acidification). The directly measured ACN blood:air PC was 437 +/- 8 (n = 8), which compared well with the estimated values. Treatment of tissues with diethyl maleate or 2,4-dinitrofluorobenzene did not abolish the active uptake of CEO. However, pretreatment of tissues with CEO itself abolished subsequent CEO uptake. The CEO blood:air PC estimates obtained from zero time extrapolation of four CEO concentrations (1672 +/- 139) and from CEO pretreatment (1658 +/- 137, n = 8) were in good agreement. These data indicate that tissue:air PCs for volatile reactive chemicals can be estimated by extrapolation of a first-order uptake process to zero time or at equilibrium following chemical modification of reactive groups in tissues.

Acrylonitrile↗

Dose-dependent urinary excretion of acrylonitrile metabolites by rats and mice.

The dose dependence of the urinary excretion of acrylonitrile (ACN) metabolites was studied after oral administration of [2,3-14C]ACN to male F-344 rats (0.09 to 28.8 mg/kg) and male B6C3F1 mice (0.09 to 10.0 mg/kg). Urine was the major route of excretion of ACN metabolites (77 to 104% of the dose), with less than 8% of the dose excreted in the feces. Reverse-phase HPLC analysis of urine from treated animals indicated five major components (1 through 5 in order of elution) that accounted for 75 to 100% of the total urinary radioactivity. Component 4 was observed in the urine of ACN-treated mice but was only present in trace amounts in the urine of ACN-treated rats. Components 1, 2, and 3 were present in the urine of animals administered [2,3-14C]cyanoethylene oxide (CEO), indicating that these components were derived from the epoxide metabolite of ACN. The ACN urinary metabolites were isolated by HPLC and identified by chromatographic and mass spectral analysis. Component 5 was N-acetyl-S-(2-cyanoethyl)cysteine and component 4 was S-(2-cyanoethyl)thioacetic acid, both derived from the glutathione (GSH) conjugate of ACN. Component 3 contained N-acetyl-S-(2-hydroxyethyl)cysteine, N-acetyl-S-(carboxymethyl)cysteine, and N-acetyl-S-(1-cyano-2-hydroxyethyl)cysteine. Component 2 was thiodiglycolic acid. These urinary metabolites are derived from catabolism of the GSH conjugates of CEO. The polar component 1 was not identified. These results demonstrate that GSH conjugation is the major disposition pathway of ACN. The excretion of metabolites derived from CEO was an approximately linear function of dose in both species, whereas the excretion of N-acetyl-S-(2-cyanoethyl)cysteine increased nonlinearly with dose. This nonlinearity indicates the presence of a saturable pathway competing with glutathione for ACN, most likely the cytochrome P450-dependent oxidation of ACN. Thiodiglycolic acid was formed 10-fold more in mice than in rats, but this species difference in the oxidative processing of GSH conjugates is probably not of toxicological significance. The ratio of ACN epoxidation to GSH conjugation was 0.50 in rats and 0.67 in mice. This species difference in ACN oxidation could have important toxicological implications, since CEO is believed to mediate the carcinogenic effects of ACN.

Acrylonitrile↗

Furan-induced cytolethality in isolated rat hepatocytes: correspondence with in vivo dosimetry.

Furan, a rodent hepatotoxicant and hepatocarcinogen, produced incubation time- and concentration-dependent decreases in the glutathione (GSH) content and viability of freshly isolated F-344 rat hepatocytes in vitro. Since furan itself did not significantly react with GSH, these data indicate the formation of a reactive metabolite of furan in hepatocyte suspensions. Treatment of the hepatocyte suspensions with the cytochrome P450 inhibitor 1-phenylimidazole delayed GSH depletion but did not alter furan-induced (4 to 12 mM) cytolethality. The furan concentrations required to produce measurable hepatocyte cytolethality in vitro within 6 hr (4 to 12 mM) were several orders of magnitude greater than the predicted maximal liver concentrations of furan in vivo following hepatotoxic doses. In order to study the mechanisms involved in the cytolethality of furan toward hepatocytes in vitro at concentrations relevant to hepatotoxicity in vivo, a hepatocyte suspension/culture system was developed that utilized furan concentrations and incubation times similar to hepatic dosimetry in vivo. Freshly isolated rat hepatocytes in suspension (in Williams' Medium E) were incubated with furan (2 to 100 microM) for 1-4 hr and placed in culture, and viability was determined after 24 hr by lactate dehydrogenase release. Furan produced cytolethality (5 to 70%) and modest GSH depletion in an incubation time- and concentration-dependent manner. Both GSH depletion and cytolethality induced by furan were prevented by 1-phenylimidazole and enhanced by acetone pretreatment of the rats. These data show that oxidation of furan by cytochrome P450 is required for GSH depletion and cytolethality, indicating that a reactive metabolite is involved in cell death. The results of this study underscore the importance of using in vivo toxicant concentrations and exposure times for in vitro mechanistic studies of chemically induced cytolethality.

Animals↗

Kinetic analysis of furan biotransformation by F-344 rats in vivo and in vitro.

Furan is both hepatotoxic and hepatocarcinogenic in rats. The kinetics of furan biotransformation by male F-344 rats were studied in vivo and in vitro in order to understand target tissue dosimetry. A physiologically based pharmacokinetic (PBPK) model for furan in rats was developed from gas uptake studies using initial furan concentrations of 100, 500, 1050, and 3850 ppm. Tissue partition coefficients for furan were determined in vitro using vial equilibration techniques. Furan gas uptake kinetics in vivo were described by a single saturable process with a Vmax of 27.0 mumol/hr/250 g rat and a KM of 2.0 microM. Furan metabolism in vivo was inhibited by pyrazole. The furan PBPK model adequately simulated blood and liver furan concentrations following 4-hr inhalation exposures to 52, 107, and 208 ppm furan. The biotransformation of furan was studied in freshly isolated rat hepatocytes in vitro and compared to biotransformation in vivo. Furan biotransformation by isolated rat hepatocytes exhibited a KM of 0.4 microM and a Vmax of 0.018 mumol/hr/10(6) cells. Inhibition and induction studies indicated that cytochrome P450 was the catalyst of furan oxidation. Acetone pretreatment of the rats produced a five-fold increase in the rate of the hepatocyte oxidation of furan, suggesting an important role for cytochrome P450 2E1. The Vmax determined in hepatocytes in vitro extrapolated to 23.0 mumol/hr/250 g rat, assuming 128 x 10(6) hepatocytes/g liver. Incorporation of the in vitro hepatocyte kinetic parameters into the PBPK model for furan accurately simulated in vivo pharmacokinetics. These results suggest that freshly isolated hepatocytes are a valuable in vitro system for predicting chemical pharmacokinetics in vivo.

Animals↗

Rodent tissue distribution of 2-cyanoethylene oxide, the epoxide metabolite of acrylonitrile.

The direct acting mutagen 2-cyanoethylene oxide (CEO), formed in the liver by oxidation of acrylonitrile (ACN), is thought to mediate the extrahepatic carcinogenic effects of ACN in rats. This study determined the tissue distribution of CEO (3 mg/kg p.o.) in F-344 rats and B6C3F1 mice. Radioactivity from [2,3-14C]CEO was widely distributed in the major organs of rodents by 2 h and decreased by 71% to 90% within 24 h, demonstrating that there was no preferential tissue uptake or retention of CEO. CEO was detected in rodent blood and brain 5-10 min after an oral dose of ACN (10 mg/kg), demonstrating that this mutagenic epoxide metabolite circulates to extrahepatic target organs following ACN administration.

Acrylonitrile↗

Species differences in the hydrolysis of 2-cyanoethylene oxide, the epoxide metabolite of acrylonitrile.

The carcinogenic effects of acrylonitrile in rats are believed to be mediated by its DNA-reactive epoxide metabolite, 2-cyanoethylene oxide (CEO). Previous studies have shown that conjugation with glutathione is the major detoxication pathway for both acrylonitrile and CEO. This study investigated the role of epoxide hydrolase in the hydrolysis of CEO by HPLC analysis of the products from [2,3-14C]CEO. CEO is a relatively stable epoxide with a half-life of 99 min at 37 degrees C in sodium phosphate buffer (0.1 M), pH 7.3. Incubation with hepatic microsomes or cytosols from male F-344 rats or B6C3F1 mice did not enhance the rate of hydrolysis of CEO (0.69 nmol/min). Human hepatic microsomes significantly increased the rate of hydrolysis of CEO, whereas human hepatic cytosols did not. Human hepatic microsomal hydrolysis activity was heat-sensitive and potently inhibited by 1,1,1-trichloropropene oxide (IC50 of 23 microM), indicating that epoxide hydrolase was the catalyst. The hydrolysis of CEO catalyzed by hepatic microsomes from six individuals exhibited normal saturation kinetics with KM ranging from 0.6 to 3.2 mM and Vmax from 8.3 to 18.8 nmol hydrolysis products/min/mg protein. Pretreatment of rodents with phenobarbital or acetone induced hepatic microsomal hydrolysis activity toward CEO, whereas treatment with beta-naphthoflavone, dexamethasone or acrylonitrile itself was without effect. These data show that humans possess an additional detoxication pathway for CEO that is not active in rodents (but is inducible). The presence of an active epoxide hydrolase hydrolysis activity toward CEO in humans should be considered in assessments of cancer risk from acrylonitrile exposure.

Animals↗

Induction of rat liver microsomal epoxide hydrolase by thiazole and pyrazine: hydrolysis of 2-cyanoethylene oxide.

Liver microsomal epoxide hydrolase (mEH) is active in the detoxification of epoxide-containing carcinogens. The effects of thiazole and pyrazine, constituents of tobacco and tobacco smoke as well as of a variety of foods, on the expression and regulation of mEH were examined in rats (200 mg/kg body wt/day, i.p., 1-3 days). Immunoblot analyses using rabbit anti-rat mEH antibody revealed a significant increase in mEH levels in hepatic microsomes isolated from either thiazole- or pyrazine-treated animals. Another protein (approximately 43 kd) cross-reacting with polyclonal mEH antibody was found to be increased concomitantly following pyrazine treatment. Northern and slot blot analyses showed substantial increases in mEH mRNA following either thiazole or pyrazine treatment. The level of mEH mRNA increased 17-fold at 24 h following thiazole treatment, relative to control. Approximately 20- and 16-fold increases in mEH mRNA were also observed at 48 and 72 h respectively following treatment with pyrazine. The level of polymerase chain reaction (PCR)-amplified mEH DNA derived from poly(A)+ RNA was clearly elevated following either thiazole or pyrazine treatment relative to that from untreated animals. Both sense and antisense strands of PCR-amplified mEH DNA were cloned into an M13mp19 phage vector in order to examine the nucleotide sequences of PCR-amplified mEH DNA derived from the poly(A)+ RNA isolated from thiazole- or pyrazine-treated animals. Sequence analyses revealed that the sequence of PCR-amplified DNA from the induced mRNA was identical to that published for mEH cDNA. Epoxide hydrolase activity toward the hydrolysis of 2-cyanoethylene oxide (CEO), the epoxide metabolite of the rat carcinogen acrylonitrile, was not significant in hepatic microsomes from untreated rats, but was substantially induced by treatment with thiazole or pyrazine. Microsomal hydrolysis activity was heat-sensitive and potently inhibited by 1,1,1-trichloropropene-2,3-oxide, indicating that mEH was the catalyst. The Vmax for the hydrolysis of CEO by hepatic microsomes from thiazole-treated rats (13.4 nmol/min/mg protein) was 1.5-fold greater than that with microsomes from pyrazine-treated rats, whereas similar Km values (approximately 1 mM) were observed for both microsomal preparations. These kinetic data correlate well with the increases in mEH mRNA observed after administration of thiazole or pyrazine to rats. These results provide evidence that administration of thiazole or pyrazine induces mEH with a large increase in mEH mRNA, and that the induced mEH catalyzes the hydrolysis of CEO.

Animals↗

Glutathione S-transferase-mediated chlorothalonil metabolism in liver and gill subcellular fractions of channel catfish.

Chlorothalonil (2,4,5,6-tetrachloroisophthalonitrile) is a broad spectrum fungicide that is a potent acute toxicant to fish. Therefore, the metabolism of chlorothalonil was investigated in liver and gill cytosolic and microsomal fractions from channel catfish (Ictalurus punctatus) using HPLC. All fractions catalyzed the metabolism of chlorothalonil to polar metabolites. Chlorothalonil metabolism by cytosolic fractions was reduced markedly when glutathione (GSH) was omitted from the reaction mixtures. The lack of microsomal metabolism in the presence of either NADPH or an NADPH-regenerating system indicated direct glutathione S-transferase (GST)-catalyzed conjugation with GSH without prior oxidation by cytochrome P450. Cytosolic and microsomal GSTs from both tissues were also active toward 1-chloro-2,4-dinitrobenzene (CDNB), a commonly employed reference substrate. In summary, channel catfish detoxified chlorothalonil in vitro by GST-catalyzed GSH conjugation in the liver and gill. The present report is the first to confirm microsomal GST activity toward CDNB in gill and toward chlorothalonil in liver, and also of gill cytosolic GST activity towards chlorothalonil, in an aquatic species.

Animals↗

Species comparison of acrylonitrile epoxidation by microsomes from mice, rats and humans: relationship to epoxide concentrations in mouse and rat blood.

Acrylonitrile (ACN) has been shown to cause tumors of the brain, stomach and Zymbal's gland in rats in several bioassays, but it has not been tested in other species. The carcinogenic risk of humans exposed to ACN is unclear. ACN is metabolized in the liver to 2-cyanoethylene oxide (CEO), which is believed to be the proximate or ultimate carcinogenic species. Therefore, the kinetics of CEO formation were studied with liver and lung microsomes from mice and humans using a GC-MS assay for CEO, and the data were compared with previously obtained kinetic parameters for rat microsomal enzymes. The rate of CEO formation by human liver microsomes was comparable to that of rat liver microsomes, but less than that of mouse liver microsomes. Liver microsomes produced more CEO than lung microsomes with all three species. CEO formation by microsomes from mice was approximately 4 times greater than that by microsomes from rats or humans, suggesting that mice would have higher CEO concentrations in blood than rats after ACN exposure. However, after oral administration of ACN, the concentration of CEO in mouse blood was one-third that in rat blood at all doses and time points examined. These results show that CEO circulates via the blood, providing exposure to distant sites. The blood concentrations of CEO do not appear to correlate with rates of microsomal CEO formation. This suggests that species differences in the detoxication of CEO may play an important role in determining circulating CEO concentrations and distant organ exposure.

Acrylonitrile↗

The role of metabolism and covalent binding in the cytotoxicity of a nitrogen-containing steroid toward rat hepatocytes.

The nitrogen-containing steroid N,N-diethyl-4-methyl-3-oxo-4-aza-5 alpha-androst-1-ene-17 beta-carboxamide (I) causes concentration- and time-dependent cytotoxicity toward freshly isolated F-344 rat hepatocytes. Because hepatocytes extensively metabolize I to both stable and reactive products, the role of metabolism and covalent binding in the cytotoxicity of I was investigated. Concentration-dependent covalent binding of I-related material to hepatocyte macromolecules was detected. Treatment of rats with phenobarbital increased the rate and extent of hepatocyte metabolism of I, increased the covalent binding of I-related material to hepatocyte macromolecules, but decreased the cytotoxicity of I. Addition of testosterone to incubations of hepatocytes and I inhibited the metabolism of I, decreased the covalent binding of I-related material to hepatocyte macromolecules, but potentiated the cytotoxicity of I. These results indicate that the covalent binding of reactive metabolites is not involved in the cytotoxicity of I. Moreover, the two major metabolites of I, the 4-carbinolamide and monoethyl analog, were much less cytotoxic toward hepatocytes than I. These data suggest that the metabolism of I represents detoxication and that the parent compound is the cytotoxicant.

Animals↗

Mechanism of reductive activation of a 5-nitroimidazole by flavoproteins: model studies with dithionite.

The flavoprotein nitroreductases NADPH:cytochrome P-450 reductase and xanthine oxidase catalyzed the cofactor-dependent anaerobic nitro group reduction and covalent binding to protein sulfhydryl groups of the 5-nitroimidazole substrate ronidazole [1-methyl-5-nitroimidazole-2-yl)-methyl carbamate). Studies with variously radiolabeled ronidazole molecules demonstrated that the imidazole ring was intact while greater than 80% of the C-4 3H and 2-carbamoyl group were lost from the covalently bound product. The stoichiometry of cofactor consumption during the enzyme-catalyzed reduction of the substrate could not be determined, so a model nitroreductase system which utilized dithionite as the reductant and agarose-immobilized cysteine as the target for alkylation was developed. Two moles of dithionite was consumed per mole of substrate for maximal reduction of uv absorbance due to the nitro group, for maximal release of C-4 3H, and for maximal covalent binding to agarose-immobilized cysteine. These results indicate that four electrons are required for the reductive activation of the substrate, consistent with formation of a hydroxylamine reactive intermediate. Covalent binding of variously radiolabeled substrate molecules after dithionite reduction exhibited the same labeling pattern as flavoprotein-catalyzed covalent binding, suggesting that covalent binding is mediated by the same species in both chemical and biological systems. The data are consistent with a mechanism where the substrate undergoes four-electron reduction to form a hydroxylamine, which is susceptible to nucleophilic attack at C-4. When water attacks C-4, the 2-carbamoyl group can eliminate to form a Michael-like acceptor which adds thiols at the 2-methylene position.

Animals↗

Studies with nitrogen-containing steroids and freshly isolated rat hepatocytes: role of cytochrome P-450 in detoxication.

Several nitrogen-containing steroids produced concentration- and time-dependent decreases in the viability of freshly isolated F-344 rat hepatocytes. N,N-Diethyl-4-methyl-3-oxo-4-aza-5 alpha-androst-1-ene-17 beta-carboxamide (I) was not cytotoxic at or below 0.3 mM but produced decreases in cell viability at higher concentrations. In contrast, the desmethyl analog of I was essentially nontoxic, demonstrating that relatively small structural changes result in substantial differences in cytotoxicity. Testosterone and other steroids specifically potentiated the cytotoxicity of I in a concentration-dependent manner, while having no effect upon the toxicity of other chemical agents. Pargyline and methimazole had no effect upon the cytotoxicity of I, suggesting that monoamine oxidase and flavin-containing monooxygenase are not involved. The cytochrome P-450 inhibitors octylamine and metyrapone potentiated the cytotoxicity of I. Induction of cytochrome P-450 isozymes by phenobarbital and beta-naphthoflavone treatment protected the cells against the cytotoxicity of I, while acetone or dexamethasone treatment had no effect. The initial rates of hepatocyte metabolism of the six nitrogen-containing steroids investigated did not correlate with cytotoxicity. Dithiothreitol and other thiol compounds had no effect upon the cytotoxicity of I, suggesting that sulfhydryl oxidation is not involved. Galactosamine and sulfate-free media had no effect upon the cytotoxicity of I. These results suggest that cytochrome P-450 is involved in the detoxication of I by rat hepatocytes while conjugative metabolism does not play a significant role.

Animals↗

18O studies of the peroxidase-catalyzed oxidation of N-methylcarbazole. Mechanisms of carbinolamine and carboxaldehyde formation.

Chloroperoxidase, horseradish peroxidase, hemoglobin, myoglobin, lactoperoxidase, and microperoxidase catalyzed the ethyl hydroperoxide-dependent oxidation of N-methylcarbazole to N-(hydroxymethyl)carbazole and N-formylcarbazole as major products. Mass spectral analysis of the N-(hydroxymethyl)carbazole formed during the peroxidase-catalyzed N-demethylation of N-methylcarbazole in 18O-enriched medium indicated partial incorporation (7.5-25.9%) of solvent water oxygen into the carbinolamine intermediate in all systems investigated, suggesting that the peroxidase active site is partially accessible to solvent water during N-demethylation. In contrast, solvent water oxygen was not incorporated into the N-formylcarbazole formed during the peroxidase-catalyzed oxidation of N-methylcarbazole. N-(Hydroxymethyl)carbazole was not further metabolized by the peroxidases in the presence of ethyl hydroperoxide, indicating that it is not an intermediate in N-formylcarbazole formation. The horseradish peroxidase-catalyzed formation of N-formylcarbazole was decreased by 77% when the hydroperoxide-supported reactions were carried out in a nitrogen atmosphere, while the formation of N-(hydroxymethyl)carbazole was decreased by 46%. When the horseradish peroxidase-catalyzed reactions were carried out in a 18O2 atmosphere, 18O incorporation into N-(hydroxymethyl)carbazole was 64.4% of the total oxygen, while 81.8% of the oxygen incorporated into N-formylcarbazole came from 18O2. These results suggest that there are two different mechanisms for the formation of N-(hydroxymethyl)carbazole, both involving the initial oxidation of N-methylcarbazole to a neutral carbon-centered radical. The radical can be further oxidized in the enzyme active site to an iminium cation, which reacts with water derived from either the oxidant or the medium to form the carbinolamine. Alternatively, the substrate radical can react with molecular oxygen to form a hydroperoxy radical, which decomposes to form the carboxaldehyde and carbinolamine.

Carbazoles↗

Kinetics of conjugation and oxidation of nitrobenzyl alcohols by rat hepatic enzymes.

Previous work has suggested that quantitative differences in the in vitro and in vivo metabolism of mononitrotoluene isomers are a result of differences in the hepatic conjugation and oxidation of the first metabolic intermediates, the mononitrobenzyl alcohols. We have determined the steady-state kinetic parameters, Vmax, Km and V/K, for the metabolism of the nitrobenzyl alcohols by rat hepatic alcohol dehydrogenase, glucuronyltransferase, and sulfotransferase. 3-Nitrobenzyl alcohol was the best substrate for cytosolic alcohol dehydrogenase (Vmax = 1.48 nmoles/min/mg protein, V/K = 3.15 X 10(-3) nmoles/min/mg protein/microM, Km = 503 microM). Vmax and Km values for 4-nitrobenzyl alcohol were similar, but V/K was about 60% of that for 3-nitrobenzyl alcohol. 2-Nitrobenzyl alcohol was not metabolized by the alcohol dehydrogenase preparation used here, but it was metabolized to 2-nitrobenzoic acid by a rat liver mitochondrial preparation. 2-Nitrobenzyl alcohol was the best substrate for microsomal glucuronyltransferase (Vmax = 3.59 nmoles/min/mg protein, V/K = 11.28 X 10(-3) nmoles/min/mg protein/microM, Km = 373 microM). The Vmax for 3-nitrobenzyl alcohol was similar, but the V/K was about half and the Km was about twice that for 2-nitrobenzyl alcohol. The Vmax for 4-nitrobenzyl alcohol was about 40% and the V/K was about half that for 2-nitrobenzyl alcohol. The best substrate for cytosolic sulfotransferase was 4-nitrobenzyl alcohol (Vmax = 1.69 nmoles/min/mg protein, V/K = 37.21 X 10(-3) nmoles/min/mg protein/microM, Km = 48 microM). The Vmax values for the other two benzyl alcohols were similar, but the V/K and Km values were about 11 and 400%, respectively, of those for 4-nitrobenzyl alcohol. These data are in qualitative agreement with results obtained when the nitrobenzyl alcohols were incubated with isolated hepatocytes, but they do not allow quantitative modeling of the data from hepatocytes.

Alcohol Dehydrogenase↗