Induction of DT-diaphorase by 2,3,7,8-tetrachlorodibenzo-p-dioxin (ICDD)

2,3,7,8-Tetrachlorodibenzo-p-dioxin induces premature activation of the KLF2 regulon during thymocyte development

The environmental pollutant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD, dioxin) causes numerous and diverse toxic events via activation of the aryl hydrocarbon receptor, including atrophy of the thymus. Exposure to TCDD induces acute thymocyte cell loss, which occurs concomitantly with proliferation arrest and premature emigration of triple negative (TN; CD4(-), CD8(-), CD3(-)) T cell progenitors. In this report, we demonstrate that TCDD exposure results in dysregulation of KLF2 (Kruppel-like factor 2) expression in developing thymocytes. The Klf2 gene encodes an Sp1-like zinc finger transcription factor that functions as a central regulator of T lymphocyte proliferation and trafficking. During normal thymocyte development, KLF2 is expressed exclusively in CD4 and CD8 single positive T cells and promotes a nonproliferative, promigratory phenotype. In mice exposed to TCDD, however, the Klf2 gene is prematurely expressed in TN thymocytes. Administration of a 100 microg/kg dose of TCDD results in a approximately 15-fold induction of KLF2 as early as the TN2 (CD44(+), CD25(+)) stage of development and immediately precedes acute cell loss in the TN3, TN4, and double positive (CD4(+), CD8(+)) cell stages. Induction of KLF2 occurs within 12 h of TCDD exposure and is fully dependent on expression of the aryl hydrocarbon receptor. In addition, TCDD exposure alters the expression of several factors comprising the KLF2 regulon, including Edg1/S1P(1), beta(7) integrin, CD52, Cdkn2d (cyclin-dependent kinase inhibitor 2D), s100a4, and IL10R alpha. These findings indicate that the pollutant TCDD interferes with early thymopoeisis via ectopic expression of the KLF2 regulon.

Effects of the agrochemicals butachlor, pretilachlor and isoprothiolane on rat liver xenobiotic-metabolizing enzymes

1. The herbicides butachlor (2-chloro-2',6',diethyl-N-[buthoxymethyl] acetanilide) and pretilachlor (2-chloro-2',6'-diethyl-N-[2-propoxyethyl] acetanilide) are widely used in Asia, South America, Europe and Africa. Isoprothiolane (diisopropyl-1,3-dithiolan-2-ylidenemalonate) is used as a fungicide and an insecticide in rice paddies. We administered these agrochemicals to the male rat and examined their effects on cytochrome P450 (P450), glutathione S-transferase (GST), UDP-glucuronosyltransferase (UDPGT), and NAD(P)H-quinone oxidoreductase 1 (NQO1)-related metabolism in the liver. 2. Administration of isoprothiolane, butachlor or pretilachlor to rat induced hepatic P4502B subfamily-dependent enzyme activities (pentoxyresorufin O-depentylation and testosterone 16 beta-hydroxylation) up to 271-413% of control, which coincided with the increase in expression levels of the P4502B apoprotein. 3. Activities of GST toward 1-chloro-2,4-nitrobenzene and 3,4-dichloronitrobenzene were slightly induced (127-133% of control) in the liver of the rat treated with these pesticides. On the other hand, marked elevations of UDPGT activities toward p-nitrophenol (164-281% of control) were observed. NQO1-related metabolism (menadione reductase activity) was also induced (123-176% of control) in the liver of rat treated with these agrochemicals. 4. These results indicate that some of the agrochemicals currently in use are capable of inducing phase I and II xenobiotic-metabolizing enzyme activities in an isozyme selective manner. The induction of these activities may disrupt normal physiologic functions related to these enzymes in exposed animals.

The effect of 1,2,3,4-tetrachlorodibenzo-p-dioxin on drug-metabolizing enzymes in the rat liver

The effects of 1,2,3,4-tetrachlorodibenzo-p-dioxin (1,2,3,4-TCDD) on drug-metabolizing enzymes were studied in male and female rats. 1,2,3,4-TCDD (25, 50, 100 and 200 mumol/kg) was administered by i.p. injection once. Among the cytochrome P-450 (P450)-mediated monooxygenase activities tested, 7-ethoxyresorufin O-deethylase (EROD) activities in both male and female rats, which are associated with CYP1A1, were remarkably induced by all doses of 1,2,3,4-TCDD. The relative induction to each control activity were from 3.0- to 24.5-fold and from 2.2- to 16.5-fold, respectively. Also, 1,2,3,4-TCDD increased other CYP1A-mediated monooxygenase activities such as 7-ethoxycoumarin O-deethylase (ECOD) and 7-methoxyresorufin O-demethylase (MROD) in male and female rats dose-dependently (1.4- to 4.3-fold). Western immunoblotting showed that the levels of CYP1A1 and CYP1A2 proteins in liver microsomes were increased by 1,2,3,4-TCDD. Although the activities of other P450-mediated monooxygenases, namely 7-pentoxyresorufin O-depentylase (PROD), 7-benzyloxyresorufin O-debenzylase (BROD), aminopyrine N-demethylase (APND) and nitrosodimethylamine N-demethylase (NDAND) in both male and female rats were induced at high doses (> or = 50 mumol/kg) of 1,2,3,4-TCDD, the relative level was low compared with those of the CYP1A-mediated monooxygenase such as EROD, ECOD or MROD. In addition to P450-mediated monooxygenase, there was significant induction in the activities of the Phase II drug-metabolizing enzymes, UDP-glucuronyltransferase (UGT) activities towards 4-nitrophenol (4-NP) and 7-hydroxycoumarin (7-HC) and glutathione S-transferase (GST) towards 1-chloro-2,4-dinitrobenzene (CDNB), 1,2-dichloro-4-nitrobenzene (DCNB) and DT-diaphorase. These results indicate that 1,2,3,4-TCDD induces both Phase I (CYP1A-mediated monooxygenase) and Phase II drug-metabolizing enzymes (UGT, GST, DT-diaphorase) in the male and female rat liver, and that the alterations of drug-metabolizing enzyme are characteristic of PCDD toxicity.

Effect of 1,2,4-trichlorodibenzo-p-dioxin on drug-metabolizing enzymes in the rat liver

The effects of 1,2,4-trichlorodibenzo-p-dioxin (1,2,4-TrCDD) on drug-metabolizing-enzymes have been studied in male Wistar rats. 1,2,4-TrCDD (0.1 mmol/kg per day) was administered by i.p. injection for 3 days. Among the cytochrome P-450 (P450)-mediated monooxygenase activities tested, 7-ethoxyresorufin O-deethylase, which is associated with CYP1A1, was remarkably induced by 1,2,4-TrCDD (0.1 mmol/kg). The relative induction to control activity was 32.9-fold. Also, 1,2,4-TrCDD increased other CYP1A-mediated monooxygenase activities such as 7-ethoxycoumarin O-deethylase, 4-nitroanisole O-demethylase, 7-methoxyresorufin O-demethylase and caffeine N-demethylase from 5.7- to 1.9-fold. Western immunoblotting showed that the levels of CYP1A1 and CYP1A2 proteins in liver microsomes were increased by 1,2,4-TrCDD. On the other hand, 7-pentoxyresorufin O-depentylase activity was induced 2.6-fold whereas aniline 4-hydroxylase, nitrosodimethylamine N-demethylase and erythromycin N-demethylase activities were increased slightly (1.3-, 1.6- and 1.3-fold, respectively) by 1,2,4-TrCDD. However, aminopyrine N-demethylase was not significantly induced by 1,2,4-TrCDD. Of the Phase II drug-metabolizing enzymes, DT-diaphorase and glutathione S-transferase (GST) activities towards 1-chloro-2,4-dinitrobenzene and 1,2-dichloro-4-nitrobenzene, and those of UDP-glucuronyltransferase (UGT) towards 4-nitrophenol and 7-hydroxycoumarin were increased from 2.7 to 1.4-fold by 1,2,4-TrCDD. These results indicate that 1,2,4-TrCDD induces both Phase I and Phase II drug-metabolizing enzymes in the rat liver.

NAD(P)H:quinone oxidoreductase1 (DT-diaphorase) expression in normal and tumor tissues

NAD(P)H:Quinone Oxidoreductase1 (NQO1) also known as DT-diaphorase is a flavoprotein that catalyzes the two-electron reduction of quinones, quinone imines and azo-dyes and thereby protects cells against mutagenicity and carcinogenicity resulting from free radicals and toxic oxygen metabolites generated by the one-electron reductions catalyzed by cytochromes P450 and other enzymes. High levels of NQO1 gene expression have been observed in liver, lung, colon and breast tumors as compared to normal tissues of the same origin. The transcription of the NQO1 gene is activated in response to exposure to bifunctional (e.g. beta-naphthoflavone (beta-NF), 2, 3, 7, 8 tetrachorodibenzo-p-dioxin (TCDD)) and monofunctional (phenolic antioxidants/chemoprotectors e.g. 2(3)-tert-butyl-4-hydroxy-anisole (BHA)) inducers. The high level of expression of the NQO1 gene and its induction by beta-NF and BHA require the presence of an AP1 binding site contained within the human Antioxidant Response Element (hARE) and are mediated by products of proto-oncogenes, Jun and Fos. Induction of NQO1 gene expression involves transfer of a redox signal from xenobiotics to unknown 'redox protein(s)' which in turn, modify the Jun and Fos proteins for greater affinity towards the AP1 site of the NQO1 gene and activates transcription. The expression and regulation of the NQO1 gene is complex as many additional cis-elements have been identified in the promoter region and is a subject of great future interest. In addition to established tumors, NQO1 gene expression is also increased in developing tumors, indicating a role in cellular defense during tumorigenesis. It has been proposed that low molecular weight substance(s) can diffuse from tumor cells into surrounding normal cells and activate the expression of the NQO1 gene. Purification and characterization of such substance(s) may provide important information in regard to the mechanism of activation of NQO1 gene expression and the role of increased NQO1 expression in tumor development. In view of the general consensus that NQO1 is over-expressed in tumor cells and the realization that NQO1 may either activate or detoxify xenobiotics, it is important to establish the role of NQO1 in the activation, and the detoxification of xenobiotics and drugs and in the intrinsic sensitivity of tumors to bioreductive alkylating aziridinyl benzoquinones such as diaziquone (AZQ), mitomycin C (MMC), and indoloquinone EO9, as well as to the dinitrophenyl aziridine, CB1954, and the benzotriazine-di-N-oxide, SR 4233.

The Ah receptor and the mechanism of dioxin toxicity

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The human dioxin-inducible NAD(P)H: quinone oxidoreductase cDNA-encoded protein expressed in COS-1 cells is identical to diaphorase 4

NAD(P)H: quinone oxidoreductase (NQO1) is believed to be protective against cancer and toxicity caused by exposure to quinones and their metabolic precursors. This enzyme catalyzes the two-electron reduction of compounds, compared with one-electron reduction mediated by NADPH: cytochrome-P450 oxidoreductase which produces toxic and mutagenic free radicals. Recently we cloned and sequenced the cDNA encoding human 2.3,7,8-tetrachlorodibenzo-p-dioxin (dioxin)-inducible cytosolic NQO1 [Jaiswal et al. (1988) J. Biol. Chem. 263, 13572-13578] and provided preliminary evidence that this enzyme may correspond to diaphorase 4, an enzymatic activity present in various tissues that catalyzes the reduction of a variety of quinones by both NADH and NADPH [Edwards et al. (1980) Biochem. J. 187, 429-436]. In the present report we characterize the catalytic properties of the protein encoded by the NQO1 cDNA. The enzyme was synthesized in monkey kidney COS-1 cells transfected with a pMT2-based expression plasmid containing the NQO1 cDNA. Western blot analysis of the transfected cells using an antibody against rat liver cytosolic NQO1 revealed a 31-kDa band that was not detected in nontransfected cells. This band corresponded to a polypeptide with the same electrophoretic mobility as the endogenous NQO1 protein detected in the human hepatoblastoma (Hep-G2) cells with the same antibody. The immunoreactive protein detected in human Hep-G2 cells was induced approximately fourfold by exposure of the cultures to dioxin, an increase commensurate with the increased in quinone oxidoreductase activity. These studies suggest that the protein encoded by NQO1 cDNA is indeed similar, if not identical, to the dioxin-inducible protein band detected in human Hep-G2 cells. Further characterization of the product of NQO1 cDNA, which was present at approximately 20-30-fold higher levels in transfected COS cells than the endogenous product in uninduced human Hep-G2 cells indicated that it had very high capacity (greater than 1000-fold over background) to catalyze the reduction of 2.6-dichloroindophenol and menadione. Besides these two commonly used substrates for quinone reductase, the expressed NQO1 protein also effectively metabolized 2,6-dimethylbenzoquinone, methylene blue, p-benzoquinone, 1,4-naphthoquinone, 2-methyl-1,4-benzoquinone, with the latter being the most potent electron acceptor at 50 microM concentration of the substrate.

NAD(P)H: quinone oxidoreductase (DT-diaphorase) in chick embryo liver. Comparison to activity in rat and guinea pig liver and differences in co-induction with 7-ethoxyresorufin deethylase by 2,3,7,8-tetrachlorodibenzo-p-dioxin

NAD(P)H:quinone oxidoreductase (EC 1.6.99.2; DT-diaphorase) was present in the liver of 18- and 19-day-old chick embryos as assayed both by reduction of resorufin and by the more traditional assay, reduction of 2,6-dichlorophenolindophenol (DCPIP). Both reductions had the classic characteristics of DT-diaphorase: they were equally supported by NADPH and NADH and almost entirely inhibited by dicumarol. Chick embryo liver DT-diaphorase was entirely cytosolic. It was undetectable in the microsomal and mitochondrial fractions. Chick embryo liver cytosol and mitochondrial fractions contained an enzyme oxidizer of resorufin but not of DCPIP. The Km for NADPH for resorufin reductase was an order of magnitude higher in chick embryo than in rat or guinea pig cytosol (1 mM vs 0.1 mM). Resorufin reductase activity was higher for chick embryo than for rat or guinea pig cytosols: Vmax (nmol resorufin reduced per mg cytosolic protein per min +/- SEM) 355 +/- 28 for chick embryo, 159 +/- 10 for guinea pig and 68 +/- 28 for rat. The Vmax for DCPIP reduction was also twice as high in chick embryo as rat liver cytosol. In the chick embryo, 7 days after treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) at 6.4 micrograms/kg egg (1 nmol/egg) mortality was increased 2.4-fold, hepatic DT-diaphorase 1.3-fold, and 7-ethoxyresorufin deethylase (7-EROD) 72-fold over control levels. At 32 micrograms/kg, mortality was increased 4.2-fold, DT-diaphorase 2.3-fold and 7-EROD 100-fold. In the guinea pig, 5 days after treatment with TCDD at 10 micrograms/kg, TCDD toxicity was also evident (loss of body weight and thymus weight); there was no change in DT-diaphorase as measured by resorufin reduction, confirming by a different assay the observation of Beatty and Neal (Biochem Pharmacol 27: 505-510, 1978) that TCDD does not induce DT-diaphorase in guinea pig liver, and 7-EROD was increased 8-fold. In contrast, in the rat, 7 days after exposure to TCDD at 10 micrograms/kg, there was no evidence of toxicity, DT-diaphorase was increased close to 7-fold and 7-EROD, 100-fold. The results demonstrate that avian liver contains DT-diaphorase and show that the extent to which DT-diaphorase is part of the pleiotypic response of the liver to an Ah (aryl hydrocarbon) receptor ligand is species dependent. They also suggest that DT-diaphorase induction and TCDD toxicity may be inversely related. The possibility that DT-diaphorase protects against TCDD toxicity and participates in species differences in sensitivity to TCDD toxicity warrants further investigation.

Characterization of NAD(P)H diaphorase from boar spermatozoa using specific monoclonal antibodies

1. After immunization of BALB/c mouse, four monoclonal antibodies against soluble NADH diaphorase from ejaculated boar spermatozoa were produced and characterized. The monoclonal antibodies were designated as follows Mab 1F2, Mab 4E2, Mab 5B8, Mab 5D8. 2. These monoclonal antibodies react with other enzyme forms-sedimentary NADH and NADPH and soluble NADPH and inhibit (although not completely) their activity. It is supposed that different forms of the enzyme share some common epitopes. 3. Treatment of ejaculated boar semen with 2O-methylcholanthrene causes an increase of the activity of the soluble diaphorase form only. 4. These results lead to the assumption that the sperm diaphorase is a dynamic enzyme system consisting of four immunologically similar isoenzymes although their functions are different.

Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations which support the development of toxic equivalency factors (TEFs)

Halogenated aromatic compounds, typified by the polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), biphenyls (PCBs), and diphenylethers (PCDEs), are industrial compounds or byproducts which have been widely identified in the environment and in chemical-waste dumpsites. Halogenated aromatics are invariably present in diverse analytes as highly complex mixtures of isomers and congeners and this complicates the hazard and risk assessment of these compounds. Several studies have confirmed the common receptor-mediated mechanism of action of toxic halogenated aromatics and this has resulted in the development of structure-activity relationships for this class of chemicals. The most toxic halogenated aromatic is 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and based on in vivo and in vitro studies the relative toxicities of individual halogenated aromatics have been determined relative to TCDD (i.e., toxic equivalents). The derived toxic equivalents can be used for hazard and risk assessment of halogenated aromatic mixtures; moreover, for more complex mixtures containing congeners for which no standards are available (e.g., bromo/chloro mixtures), several in vitro or in vivo assays can be utilized for hazard or risk assessment.

Effects of commercial chlorophenolate, 2,3,7,8-TCDD, and pure phenoxyacetic acids on hepatic peroxisome proliferation, xenobiotic metabolism and sister chromatid exchange in the rat

The induction of hepatic peroxisome proliferation and drug metabolizing enzymes and of sister chromatid exchange (SCE) in lymphocytes was studied in male Han/Wistar rats after exposing them for 2 weeks to a commercial chlorophenolate formulation (Ky-5) (100 mg/kg/day), to 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD; 0.05-5 micrograms/kg/wk) and to the pure phenoxyacetic acids, 2,4-dichlorophenoxyacetic acid (2,4-D; 100 mg/kg/day) and 2-chloro-4-methylphenoxyacetic acid (MCPA; 100 mg/kg/day). The chlorophenolate formulation and pure 2,4-D and MCPA caused significant increases in the number of peroxisomes in liver cells, although the average size of peroxisomes was not affected, whereas the effect of even the highest dose of 2,3,7,8-TCDD remained small. This finding indicates that dioxin impurities do not account for the peroxisome proliferation induced by chlorophenolate. The relative weight of the liver increased significantly in rats treated with the chlorophenolate formulation and with 2,3,7,8-TCDD (5.0 and 0.5 micrograms/kg). The pattern of induction of xenobiotic metabolizing enzymes showed some differences between chlorophenolate treatment and 2,3,7,8-TCDD treatment. Furthermore, the effects of pure phenoxyacetic acids were different from that seen with chlorophenolate and 2,3,7,8-TCDD. The highest dose of 2,3,7,8-TCDD increased the frequency of SCE in circulating lymphocytes slightly, but significantly.

2,3,7,8-Tetrachlorodibenzo-p-dioxin causes elevation of the levels of the protein tyrosine kinase pp60c-src

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) has been found to cause increases in cellular levels of pp60src, a protein tyrosine kinase in hepatocytes from the rat and guinea pig, in the thymus of the mouse in vivo and in NIH-3T3 mouse fibroblast cell lines in vitro. Such cellular changes take place in vivo at early stages of TCDD poisoning (as early as one day after treatment in the case of mouse thymus) and at very low doses (single intraperitoneal injections of 1 microgram/kg for guinea pigs, 25 micrograms/kg for rats, and 30 micrograms/kg for mice). In addition such an effect of TCDD was observed only in a TCDD-responsive mouse strain but not in a nonresponsive strain. This effect of TCDD is a long-lasting one (eg, even 25 days after single dosing, the levels of pp60src in the hepatic membrane remained high). In vitro this effect was observed in a wild-type 3T3 cell line but was more pronounced in one of the transfected lines with a v-src gene, a virus-derived oncogene known to code for pp60src protein.

Effect of thyroid hormones on liver microsomal enzyme induction in rats exposed to 2,3,7,8,-tetrachlorodibenzo-p-dioxin

The effect of thyroidectomy and thyroid hormone replacement therapy on liver microsomal enzyme induction was studied in 2,3,7,8,-tetrachlorodibenzo-p-dioxin (TCDD)-treated rats (100 micrograms/kg). Treatment of non-thyroidectomized rats with TCDD had no effect on the concentration of liver microsomal cytochrome b5. In contrast, cytochrome b5 content was increased by TCDD treatment of thyroidectomized rats, regardless of replacement therapy with either T3 or T4. TCDD treatment increased the concentration of cytochrome P-450 (2-3-fold) and the activities of benzo[a]pyrene hydroxylase (4-7-fold), ethoxyresorufin O-de-ethylase (50-70-fold) and UDP-glucuronosyltransferase (5-7-fold) in non-thyroidectomized and thyroidectomized as well as thyroidectomized thyroid hormone treated rats; indicating the induction of these liver microsomal enzyme activities is independent of thyroid status. Because thyroid status alters the toxicity of TCDD but does not alter the ability of TCDD to induce microsomal enzymes, it appears that TCDD toxicity may not be directly related to microsomal enzyme induction.

The role of receptors in 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxicity

There is good evidence that the Ah-(TCDD-) receptor plays a role in the toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and its congeners. TCDD and other chlorinated aromatic hydrocarbons with chlorine atoms in lateral positions (2,3,7,8-tetrachlorodibenzofuran, 3,3',4,4'-tetrachloroazoxybenzene, 3,3',4,4'(5,5')-tetra(hexa)chlorobiphenyl), all bind to the receptor and show a similar pattern of toxicity, although there is a wide range in potency. The Ah-receptor is viewed as the major product of the regulatory gene of the Ah-locus in the mouse. Several of the toxicities of TCDD and congeners (teratogenesis, thymic involution and hepatic porphyria) have been shown to segregate with the Ah-locus. In vitro studies using keratinizing cells or fetal thymus organ culture have shown a good correlation between activity as ligands of the receptor and toxicity for the compounds discussed. The great differences in toxic potency of these compounds in vivo may therefore be a result of variation in rate of metabolism and excretion rather than differences in affinity for the Ah-receptor. The physiological role of the Ah-receptor is discussed, whether it has developed as a response to exposure to toxic substances in the environment, as a means of induction of P-450-dependent polysubstrate mono-oxygenase activities in order to make those substances more liable for excretion--or is there a physiological ligand? TCDD has a long half-life in the body, and a sustained competition for binding to the receptor between TCDD and a ligand of importance for normal cell functions may result in toxicities such as the wasting syndrome. This tentative ligand could be of varying importance in different species, which might explain the great variation in sensitivity between species, the hamster being about 5000 times less sensitive than the guinea pig.

Cytosol-mediated reduction of resorufin: a method for measuring quinone oxidoreductase

The reduction of resorufin (7-hydroxyphenoxazone) fluorescence was catalyzed by enzymes present in the hepatic cytosol of rats and hamsters. This reaction was mediated by either NADH or NADPH, was completely inhibited by 10 microM dicumarol, and was not affected by anaerobic conditions (purging the reaction cuvette with nitrogen). The enzyme-mediated decrease in resorufin fluorescence was also associated with the loss of the primary absorbance maximum at 570 nm as well as the shoulders at 530 and 600 nm. Similar spectral changes were observed after resorufin was nonenzymatically reduced by sodium dithionite. The enzymatic activity was induced 20- to 40-fold by animal pretreatment with Aroclor-1254 or methylcholanthrene, but only minimally by phenobarbital. A 2.5-fold increase in the rate of the reaction was noted when the pH of the reaction mixture was lowered from pH 7.5 to 6.0. This pH optimum was not a result of slower rates of reoxidation of the reduced resorufin at lower pH, but was due to increased rates of reduction of the compound. Several of the characteristics of the reaction were congruent with the involvement of DT-diaphorase (quinone oxidoreductase, EC 1.6.99.2), and this newly developed fluorimetric assay would appear to be a rapid, sensitive, and direct method for measurement of DT-diaphorase activity.

Increased urinary D-glucaric acid excretion by children living in an area polluted with tetrachlorodibenzoparadioxin (TCDD)

Extremely small doses of TCDD have been shown to induce hepatic microsomal enzymes in animals. Whether levels of environmental exposure to TCDD were sufficient to produce enzyme induction in man, has been investigated in Seveso, where in July 1976 explosion in a factory spread toxic substances, one of which was TCDD, to the surrounding area. The hepatic microsomal enzyme activity was assessed by estimating urinary d-glucaric acid (UGA) excretion in children 6-8 years old. In 31 children, urine samples were collected between August and December 1976; in 67 other children in February 1979. As a control group 60 children living in Busto Arsizio (a small industrial town near Milan) and 26 living Cannero (a non-industrialized village on Lake Maggiore) were chosen. In the first period of collection, children with chloracne (which is considered to be a characteristic manifestation of intoxication with chlorinated products), showed significantly increased levels of UGA compared with children without chloracne. In 1979, children living in the Seveso area showed a statistically significant enhancement of d-glucaric acid excretion compared to the control groups. In conclusion, this study demonstrates that many children living in the Seveso area have an increased activity of hepatic microsomal enzymes, since, although the urinary excretion of d-glucaric acid is only an indirect measure of enzyme activity, studies in man have indicated that it is both sensitive and quantitative. As far as the cause of this increase is concerned, since it is possible to exclude the influence of alcohol, contraceptives, phenobarbitone or other drugs, it is reasonable to conclude that TCDD, a potent inducer agent, could be responsible for this phenomenon.

Elevation of quinone reductase activity by anticarcinogenic antioxidants

NAD(P)H:quinone reductase exhibits broad specificity in the reduction of endogenous and exogenous quinones and quinone imines, such as those derived from polycyclic aromatic carcinogens, phenolic steroids, vitamin K, and numerous therapeutic drugs. This enzyme is found in several cell compartments and is widely distributed among tissues. In contrast to several other flavoprotein dehydrogenases, quinone reductase catalyzes obligatorily two electron reductions. Extensive studies by Huggins and by others have shown that the quinone reductase in liver and some other tissues of rats is inducible by various polycyclic hydrocarbons and aromatic amines, as well as by certain azo dyes. Huggins perceived that the relative effectiveness of such compounds in inducing quinone reductase correlated with their abilities to protect against toxicity and carcinogenesis. Certain antioxidants are also known to protect against the tumorigenic and toxic effects of carcinogens. Studies on the mechanisms underlying the protective effects of BHA, BHT, ethoxyquin, and disulfiram have revealed that these compounds alter the activity profiles of several enzymes which metabolize carcinogenic and toxic compounds. We have observed that quinone reductase specific activity is increased markedly in mouse liver and several extrahepatic tissues in response to dietary BHA, ethoxyquin, and disulfiram, whereas BHT has been shown by others to enhance this enzymatic activity in rat liver. These findings confirm and extend the correlation between the ability to elevate quinone reductase activity and to confer protection against carcinogenesis and toxicity. The broad specificity of quinone reductase, its apparent inability to catalyze one electron reductions of quinones, its widespread distribution, and its inducibility by a variety of structurally dissimilar protective compounds, suggest that quinone reductase may play a significant local protective role in various regions of the cell.

Increase of NAD(P)H:quinone reductase by dietary antioxidants: possible role in protection against carcinogenesis and toxicity

2(3)-tert-Butyl-4-hydroxyanisole (BHA) is one of several widely used antioxidant food additives that protect against chemical carcinogenesis and toxicity. The present report concerns the enhancement of dicoumarol-inhibited NAD(P)H:quinone reductase [NAD(P)H dehydrogenase (quinone); NAD(P)H:(quinone acceptor) oxidoreductase, EC 1.6.99.2] activity in mouse tissues in response to dietary administration of BHA. Cytosolic quinone reductase specific activity was increased significantly in 10 of 15 tissues examined from BHA-fed mice. The greatest proportionate increase, to 10 times control levels, was observed in liver. BHA also increased the quinone reductase activities of kidney, lung, and the mucosa of the upper small intestine severalfold. The increases of quinone reductase activities in liver and digestive tissues in response to BHA were comparable to the increases previously observed in glutathione S-transferase (EC 2.5.1.18) and epoxide hydratase (EC 3.3.2.3) activities. Quinones are among the toxic products of oxidative metabolism of aromatic hydrocarbons. NAD(P)H:quinone reductase exhibits broad specificity for structurally diverse hydrophobic quinones and may facilitate the microsomal metabolism of quinones to readily excreted conjugates. The protective effects of BHA appear to be due, at least in part, to the ability of this antioxidant to increase the activities in rodent tissues of several enzymes involved in the nonoxidative metabolism of a wide variety of xenobiotics.

Possible correlation between induction modes of hepatic enzymes by PCBs and their toxicity in rats

Acute toxicity of individual PCBs, which were categorized as either phenobarbital (PB)- or 3-methylcholanthrene (MC)-type inducers, was examined in young male Wistar rats, comparing their effects on growth rate, organ weight and liver lipid content, 5 days after a single i.p. injection. PB-type PCBs (2,4,3',4'- and 2,5,2'5'-tetrachlorobiphenyl), which slightly increased a content of cytochrome P450, did not show any significant toxicity at a dose of 100 mg/kg. On the contrary, MC-type PCBs (3,4,5,3',4'-pentachloro- and 3,4,5,3',4',5'-hexachlorobiphenyl), which markedly increased a content of cytochrome P448, strongly reduced growth rate and weights of thymus and spleen at a dose of 10 mg/kg. Liver enlargement accompanied by fatty liver was also observed only with MC-type PCBs. 3,4,3',4'-Tetrachlorobiphenyl was also toxic at a dose of 50 mg/kg, in keeping with its weak MC-type-inducing ability. Pretreatment with MC affected neither growth rate, spleen weight, nor liver lipid content. These results suggest that the toxic potency of PCBs is related to their MC-type inducing ability, but the toxic characteristics are different from those of MC itself.