Gene/Protein Disease Symptom Drug Enzyme Compound
Pivot Concepts: Gene/Protein Disease Symptom Drug Enzyme Compound   Target Concepts: Gene/Protein Disease Symptom Drug Enzyme Compound

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Query: EC:1.6.5.2 (NQO1)
6,196 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

The carcinogens, N-acetyl-aminofluorene, 7,12-dimethylbenzanthracene, 3,4-benzpyrene and 3-methylcholanthrene, increase the activity of the soluble enzyme D-T-diaphorase. This action is observed 24 h after the administration of these chemicals to rats. Dicumarol blocks this effect. Dicumarol does not inhibit the increase in activity of the microsomal aryl hydrocarbon hydroxylase system as elicited by 3,4-benz(a)pyrene and 3-methylcholanthrene. The functional significance of these findings and the possible role of cytosolic enzymic changes in chemical toxicity are discussed.
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PMID:Carcinogens and dicumarol: opposite effects on rat liver NAD(P)H dehydrogenation. 8 Nov 30

The development of cytosolic DT-diaphorase--NAD(P)H dehydrogenase, quinone, EC 1.6.99.2--and its induction by benzo(a)pyrene has been studied in rat liver. DT-diaphorase belongs to the late suckling cluster, because the largest increase in activity can be observed 18 days after birth. A considerable activity is present, however, in the neonatal period. The activity of the enzyme can be prematurely induced by benzo(a)pyrene. A lag phase of 10 h can be observed before the activity of DT-diaphorase starts to increase. This increase in activity proved to be sensitive to inhibitors of mixed-function oxydase and RNA and DNA synthesis.
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PMID:The development of DT-diaphorase in rat liver and its induction by benzo(a)pyrene. 73 48

The stimulation of reduced-NAD(P):menadione oxidoreductase (EC 1.6.99.2) activity in liver cytosol is highly correlated with the stimulation of hepatic microsomal aryl hydrocarbon (benzo[a]pyrene) hydroxylase (EC 1.14.14.2) activity in 3-methylcholanthrene-, beta-naphthoflavone-, phenobarbital-, or pregnenolone-16alpha-carbonitrile-treated inbred C57BL/6N and DBA/2N mice and in eight other inbred strains treated with 3-methylcholanthrene. No oxidoreductase activity is detectable in mouse liver microsomes. Cytochrome c and 2,6-dichlorophenolindophenol are equally good electron acceptors for the oxidoreductase. There is no preferential in vitro inhibition of induced versus control oxidoreductase activities by either alpha-naphthoflavone or metyrapone. In 3-methylcholanthrene-treated F1 and F2 progeny and offspring from backcrosses between the F1 and either C57BL/6N or DBA/2N parent, however, there is not a strict correlation between induced or noninducible aryl hydrocarbon hydroxylase and oxidoreductase activities. 2,3,7,8-Tetrachlorodibenzo-p-dioxin, at doses (80 mug kg-1) sufficiently high to induce the hydroxylase almost as well in DBA/2N as in C57BL/6N mice, induces the oxidoreductase about 3-fold in C57BL/6N and less than 50% in DBA/2N mice. All the data are consistent with an hypothesis that two loci (Ox-1 and Ox-2) regulate oxidoreductase induction by 3-methylcholanthrene, that one of the genes is linked to the Ah locus (with an estimated recombination frequency between 2% and 23%), and that the other gene is not linked to the Ah locus. These experimental data might be useful in the protein activator hypothesis of the Britten-Davidson model for gene regulation.
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PMID:Genetic differences in induction of cytosol reduced-NAD(P):menadione oxidoreductase and microsomal aryl hydrocarbon hydroxylase in the mouse. 83 15

Rats were treated with 3-methylcholanthrene (MC) and DT-diaphorase from liver was partially purified on an azodicoumarol-Sepharose 6B column and applied to an FPLC-chromatofocusing column in order to resolve isoforms. Six peaks showing significant DT-diaphorase activity were eluted from this column with a pH gradient between 7.30 to 4.80. The amino acid compositions of the two major peaks (II and VIb) were found to be nearly identical, suggesting existence of isoforms rather than isozymes of DT-diaphorase. The isoforms of DT-diaphorase showed broad substrate specificities towards four different quinones (menadione, vitamin K-1, benzo(a)pyrene 3,6-quinone and cyclized-dopamine ortho-quinone), although quantitative differences in the specific activities were also found. All isoforms are glycoproteins but contain different carbohydrates. Thus isoform II reacts with biotinylated lectins which are specific for N-acetylgalactosamine, mannose, fucose and galactosyl(beta-1,3)N-acetylgalactosamine, while isoform VIb reacts only with biotinylated lectins specific for mannose and N-acetylgalactosamine. Separation of DT-diaphorase isoforms from control rat liver cytosol using FPLC-chromatofocusing revealed that the induction of the isoforms is not uniform, since isform II was not found and the major isoform was composed of three peaks, whereas the major isoform of DT-diaphorase from liver cytosol of rats treated with 3-methylcholanthrene was composed of only two peaks.
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PMID:Separation and characterization of isoforms of DT-diaphorase from rat liver cytosol. 137 30

The c14CoS/c14CoS mouse has a homozygous deletion of about 1.2 cM on chromosome 7 that includes the albino (c) locus. The untreated 14CoS/14CoS newborn has been reported to exhibit a marked transcriptional activation of the hepatic NAD(P)H:menadione oxidoreductase (Nmo-1; DT diaphorase; quinone reductase; azo dye reductase) gene, as well as elevated UDP glucuronosyl-transferase (UGT1*06) and glutathione transferase (GT1) activities, when compared with the cch/cch wild-type and the cch/c14CoS heterozygote. We show here that the newborn hepatic activities of seven enzymes that play a role in the oxidative stress response--NMO1, UGT1*06, GT1, copper-zinc superoxide dismutase, glutathione peroxidase, glutathione reductase, and glucose-6-phosphate dehydrogenase--are increased 1.5- to 25-fold in 14CoS/14CoS, as compared with ch/ch and ch/14CoS mice. The activities of four additional enzymes having no known association with the oxidative stress response--benzo[a]pyrene hydroxylase (CYP1A1, cytochrome P(1)450), acetanilide 4-hydroxylase (CYP1A2, cytochrome P(3)450), lactate dehydrogenase (LDH), and NADPH-cytochrome c reductase--are not significantly different among the three genotypes. These data suggest that there exists an "oxidative stress" response in the untreated 14CoS/14CoS newborn. We postulate that a chromosome 7 regulatory gene, which we have named Nmo-1n, might encode a trans-acting negative effector of the Nmo-1 gene, and genes corresponding to the other elevated enzymic activities described above. When both copies of Nmo-1n are deleted, as is the case in 14CoS/14CoS mice, a battery of genes involved in oxidative stress is released from negative control and becomes activated--despite the absence of any apparent oxidative insult by foreign chemicals.
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PMID:"Oxidative stress" response in liver of an untreated newborn mouse having a 1.2-centimorgan deletion on chromosome 7. 154 Jan 61

A highly active preparation of rat liver dihydrodiol/3 alpha-hydroxysteroid dehydrogenase was obtained using a newly developed, rapid purification scheme involving affinity chromatography on Red Sepharose. Depending on the coenzyme present, the purified enzyme was found to catalyse the oxidation of dihydrodiols and steroids or the reduction of substrates with carbonyl or quinone moieties. Using a wide range of synthetic quinones derived from polycyclic aromatic hydrocarbons (PAHs), we observed a pronounced regioselectivity of the quinone reductase activity. Good substrates were the o-quinones of phenanthrene, benz(a)anthracene, chrysene and benzo(a)pyrene with the quinonoid moiety in the K-region which were reduced at rates of 1-10 mumol/min.mg enzyme. 1,4-Benzoquinone, naphthalene-1,2-quinone and benz(a)anthracene-8,9-quinone were also reduced at high rates. In contrast, alkyl-substituted quinones such as duroquinone and menadione were poor substrates for the enzyme. During the enzymatic reduction of several o-quinones, but not 1,4-benzoquinone, we observed the oxidation of large amounts of NADPH and the consumption of molecular oxygen which is indicative of a redox-cycling process. Thus, the reduction of quinones of PAHs may lead to a facilitated conjugation and excretion of these highly lipophilic compounds, but may also initiate toxic processes due to the formation of reactive oxygen species.
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PMID:Quinone reduction and redox cycling catalysed by purified rat liver dihydrodiol/3 alpha-hydroxysteroid dehydrogenase. 164 48

Specimens of the seawater fish annular seabream (Diplodus annularis) were caught from a polluted harbor area and from a clean reference area. Seawater concentrates and fish-muscle extracts were not mutagenic in the Salmonella reversion test. Liver preparations of fish from the 2 sources were comparatively assayed for microsomal mixed-function oxidases and cytosolic biochemical parameters, as well as for the ability of S12 fractions to activate promutagens or to detoxify direct-acting mutagens. A shift of the cytochrome P-450 peak from 450.3 to 448.5 was accompanied by a 4.5-fold increase in arylhydrocarbon hydroxylase activity in fish living in the polluted environment. At the same time, glucose 6-phosphate dehydrogenase and 6-phosphogluconate dehydrogenase were doubled in the cytosol of the same animals, while reduced glutathione (GSH) peroxidase and GSH S-transferase were slightly yet significantly depressed. No significant difference was recorded for other biochemical parameters, including GSH, oxidized glutathione (GSSG) reductase, NADH- and NADPH-dependent diaphorases, and DT diaphorase. In parallel, fish exposed to polluted seawater exhibited a significant and marked enhancement of the metabolic activation of the pyrolysis product Trp-P-2 and of benzo[a]pyrene-trans-7,8-diol, and at the same time were less efficient in detoxifying the antitumor compound ICR 191. Liver S12 fractions from both sources efficiently decreased the direct mutagenicity of sodium dichromate, and failed to activate benzo[a]pyrene and aflatoxin B1 to mutagenic metabolites. These results provide evidence that both biochemical parameters and the overall capacity of fish liver to activate or detoxify certain mutagens can be assumed to be sensitive indicators of exposure to mixed organic pollutants in the marine environment.
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PMID:Enhanced liver metabolism of mutagens and carcinogens in fish living in polluted seawater. 170 59

Biotransformation in carcinogen-induced diploid and polyploid hepatocytes was studied using isozyme-selective substrates for several enzyme pathways. Diploid hepatocytes were induced by partial hepatectomy, a single injection of diethylnitrosamine, and 4 weeks of 2-acetylaminofluorene (2-AAF) feeding. Then, after an additional 3-5 weeks on the control diet, diploid and polyploid hepatocytes were separated from freshly isolated hepatocytes by centrifugal elutriation. Benzo(a)pyrene hydroxylase, ethoxyresorufin O-deethylase, and methoxycoumarin O-demethylase activities were approximately 15-40% lower in the diploid hepatocyte fraction than in the polyploid cell fraction. Activities of 1-chloro-2,4-dinitrobenzene, glutathione S-transferase, 3-hydroxy-benzo(a)pyrene or 4-hydroxybiphenyl UDP-glucuronosyltransferase, and DT-diaphorase were not different in the two cell fractions. Determination of activity during the 2-AAF treatment indicated that 2-AAF increased 7-ethoxyresorufin O-deethylase and 3-hydroxybenzo(a)pyrene glucuronosyltransferase activities by 300 and 200%, respectively, in both the diploid and polyploid hepatocyte fractions. Administration of phenobarbital for 4 days at the end of the control diet period increased ethoxyresorufin and methoxycoumarin dealkylations by 2- and 4-fold, and 3-hydroxybenzo(a)pyrene glucuronidation and 1-chloro-2,4-dinitrobenzene conjugation with glutathione by 1.5- to 2-fold in both hepatocyte fractions. Slight increases in benzo(a)pyrene hydroxylation and 4-hydroxybiphenyl glucuronidation were also evident in diploid cells. Although there is a slight decrease in cytochrome P-450-dependent monooxygenase activities, these data indicate that carcinogen-induced diploid hepatocytes do not show the typical toxicant-resistant phenotype observed in preneoplastic hepatocytes of altered liver foci, which are characterized by large decreases in monooxygenase biotransformations as well as increased activities of several phase II enzymes. This finding is compatible with the hypothesis that 2-AAF-induced nonploidizing growth of diploid hepatocytes is caused by nontoxic mechanisms in the present experimental paradigm. In addition, carcinogen-induced diploid cells respond to phenobarbital in a manner similar to that of polyploid hepatocytes.
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PMID:Biotransformation in carcinogen-induced diploid and polyploid hepatocytes separated by centrifugal elutriation. 173 74

We observed previously that polychlorinated biphenyl (PCB) could be classified to two groups, 3-methylcholanthrene (MC)-type and phenobarbital (PB)-type, in term of inducibility of the hepatic enzymes. MC-type PCBs such as 3,4,3',4'-tetrachlorobiphenyl (TCB), 3,4,5,3',4'-pentachlorobiphenyl (PenCB) and 3,4,5,3',4',5'-hexachlorobiphenyl (HexCB) exhibited high acute toxicity in parallel with their induction ability of microsomal benzo[a]pyrene 3-hydroxylase and cytosolic DT-diaphorase. On the contrary, PB-type PCBs such as 2,5,2',5'-TCB and 2,4,5,2',4',5'-HexCB which induce microsomal benzphetamine N-demethylase and NADPH-cytochrome P-450 reductase activities showed virtually no or very low toxicity. In the present study, we examined effects of 2,5,2',5'-TCB and its major metabolite 3-hydroxy-2,5,2',5'-TCB on body weight gain, organ weights and activities of hepatic enzymes in rats and assessed acute toxicity of these compounds. As the results, in both 2,5,2',5'-TCB and 3-hydroxy-2,5,2',5'-TCB groups, the body weights were increased during the experiment, but the rate of growth was significantly suppressed after 3 days. Significant hypertrophy of the liver and decrease of total liver lipid content were observed in 2,5,2',5'-TCB group, but the atrophy of spleen and thymus was not affected in both groups. On the other hand, in 2,5,2',5'-TCB group, benzo[a]pyrene 3-hydroxylase and benzphetamine N-demethylase activities were increased to 2. 4-fold and 1.5-fold, respectively, but were not increased in 3-hydroxy-2,5,2',5'-TCB group. After injection of 2,5,2',5'-TCB, 45% of the dose was excreted as 3-hydroxy-2,5,2',5'-TCB in feces for 5 days.(ABSTRACT TRUNCATED AT 250 WORDS)
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PMID:[Toxicological assessment of 2,5,2',5'-tetrachlorobiphenyl and its major metabolite, 3-hydroxy-2,5,2',5'-tetrachlorobiphenyl in rats]. 191 87

Acute toxicity, inductive effects of liver enzymes and liver persistency of 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PenCDD) were compared with those of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) using male Wistar rats. 1,2,3,7,8-PenCDD treatment at a dose of 0.1 mumol/kg resulted in significant depression of growth of rats from a day to 28 days after treatment. However, the effect was relatively less than that of 2,3,7,8-TCDD. On 5 days, similarly to 2,3,7,8-TCDD-treated group, liver hypertrophy and thymic atrophy were observed in 1,2,3,7,8-PenCDD-treated groups. In addition, 1,2,3,7,8-PenCDD showed potent 3-methylcholanthrene-type inducing ability. For example, the activities of benzo(a)pyrene 3-hydroxylase and DT-diaphorase were 25-fold and 10-fold of control, respectively. On 30 days, about 50% of the inductive effects on 5 days were maintained in both 1,2,3,7,8-PenCDD- and 2,3,7,8-TCDD-treated groups. Amount of 1,2,3,7,8-PenCDD distributed to the liver on 5 days was about 80-90% of dose and was about 1.5 times greater than that of 2,3,7,8-TCDD. About 50% of dose of 1,2,3,7,8-PenCDD remained even on 30 days after treatment. From these results, it is suggested that 1,2,3,7,8-PenCDD possessing the potent acute toxicity comparable to 2,3,7,8-TCDD and higher persistency in the liver might be more important than 2,3,7,8-TCDD in terms of the chronic toxicity.
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PMID:[Acute toxicity, inductive effects of liver enzymes and distribution in the liver of 1,2,3,7,8-pentachlorodibenzo-p-dioxin in rats]. 191 88


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