Factors affecting the induction of DT-diaphorase by 2,3,7,8-tetrachlorodibenzo-p-dioxin

Biochemical biomarkers in algae and marine pollution: a review

Environmental pollution by organic compounds and metals became extensive as mining and industrial activities increased in the 19th century and have intensified since then. Environmental pollutants originating from diverse anthropogenic sources have been known to possess adverse values capable of degrading the ecological integrity of marine environment. The consequences of anthropogenic contamination of marine environments have been ignored or poorly characterized with the possible exception of coastal and estuarine waters close to sewage outlets. Monitoring the impact of pollutants on aquatic life forms is challenging due to the differential sensitivities of organisms to a given pollutant, and the inability to assess the long-term effects of persistent pollutants on the ecosystem as they are bio-accumulated at higher trophic levels. Marine microalgae are particularly promising indicator species for organic and inorganic pollutants since they are typically the most abundant life forms in aquatic environments and occupy the base of the food chain. We review the effects of pollutants on the cellular biochemistry of microalgae and the biochemical mechanisms that microalgae use to detoxify or modify pollutants. In addition, we evaluate the potential uses of microalgae as bioindicator species as an early sentinel in polluted sites.

The toxicokinetics and metabolism of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) and their relevance for toxicity

This article reviews the present state of the art regarding the toxicokinetics and metabolism of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs). The absorption, body distribution, and metabolism can vary greatly between species and also may depend on the congener and dose. In biota, the 2,3,7,8-substituted PCDDs and PCDFs are almost exclusively retained in all tissue types, preferably liver and fat. This selective tissue retention and bioaccumulation are caused by a reduced rate of biotransformation and subsequent elimination of congeners with chlorine substitution at the 2,3,7, and 8 positions. 2,3,7,8-Substituted PCDDs and PCDFs also have the greatest toxic and biological activity and affinity for the cytosolic arylhydrocarbon (Ah)-receptor protein. The parent compound is the causal agent for Ah-receptor-mediated toxic and biological effects, with metabolism and subsequent elimination of 2,3,7,8- substituted congeners representing a detoxification process. Congener-specific affinity of PCDDs and PCDFs for the Ah-receptor, the genetic events following receptor binding, and toxicokinetics are factors that contribute to the relative in vivo potency of an individual PCDD or PCDF in a given species. Limited human data indicate that marked species differences exist in the toxicokinetics of these compounds. Thus, human risk assessment for PCDDs and PCDFs needs to consider species-, congener-, and dose-specific toxicokinetic data. In addition, exposure to complex mixtures, including PCBs, has the potential to alter the toxicokinetics of individual compounds. These alterations in toxicokinetics may be involved in some of the nonadditive toxic or biological effects that are observed after exposure to mixtures of PCDDs or PCDFs with PCBs.

Effects of acute sodium arsenite administration on the pulmonary chemical metabolizing enzymes, cytochrome P-450 monooxygenase, NAD(P)H:quinone acceptor oxidoreductase and glutathione S-transferase in guinea pig: comparison with effects in liver and kidney

Tissue specific changes in the cytochrome P-450 (P-450) monooxygenase system were observed following a single subcutaneous dose of sodium arsenite (75 mumol/kg), a known inducer of stress proteins. P-450 monooxygenase activities were assayed with several isozyme selective substrates; 7-ethoxyresorufin, 7-pentoxyresorufin, 4-aminobiphenyl and erythromycin. Both tissue selective and isozyme selective changes in monooxygenase activity were noted. For example, the rate of 4-aminobiphenyl N-hydroxylation (ABH) was increased by arsenite administration in lung but not in liver. Arsenite inhibited 7-ethoxyresorufin O-deethylation (ERF) in all tissues of control animals, but to a lesser extent in lung. However, increases of ERF activity occurred after arsenite treatment in lung of beta-naphthoflavone (beta NF)-treated guinea pigs whereas arsenite decreased ERF activities in the kidney and liver of these animals. These complex effects on ERF activity may in part be modulated by induction of heme oxygenase, whose activity was increased 2.5-3.5-fold in these organs by arsenite. The highest heme oxygenase activity was found in kidney with lower activities being present in liver and lung, respectively. These data are consistent with the decreased P-450 content observed in kidney and liver microsomes of arsenite treated guinea pigs. On the other hand there was either no change or a slight increase (about 2-fold) in the pulmonary microsomal P-450 content of these animals. A complex pattern of induction for the non-heme, Ah locus associated enzyme, NAD(P)H:quinone acceptor oxidoreductase (QOR) was also observed. With menadione as substrate arsenite treatment increased QOR activity in all tissues studied. However, with dichlorophenolindophenol (DCPIP) as substrate a significant arsenite effect was observed only in the kidney. Significant differences between the QOR substrates were also observed in beta NF-treated guinea pigs and control animals. Our results are consistent with the presence of more than one form of QOR in the guinea pig. Arsenite treatment also caused an increase in glutathione S-transferase activity, with 2,4-dinitro-1-chlorobenzene (DNCB) as substrate, of guinea pig kidney but not liver or lung.

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.

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.

Dose-dependent neurochemical changes during short-term inhalation exposure to m-xylene

Male Wistar were exposed to m-xylene vapor at concentrations of 2.0, 16.1, and 30.3 mumol/1 for 2 weeks (5 days a week, 6 h daily). Xylene concentrations in brain and perirenal fat increased between weeks 1 and 2 of exposure, in proportion to the exposure concentrations. Increase in brain NADPH-diaphorase and azoreductase activities was seen after week 2 at the two higher exposure levels, while superoxide dismutase activity decreased in a dose-related manner at the same time. Biochemical analyses on rats withdrawn from exposure for 2 weeks indicated that the biochemical effects were largely abolished within that time, although cerebral RNA was above the control value at the two higher exposure levels.

Behavioural and glial cell effects of inhalation exposure to styrene vapour with special reference to interactions of simultaneous peroral ethanol intake

Male Wistar rats were exposed to 300 p.p.m. of styrene vapour with simultaneous ethanol ingestion for 4 to 17 weeks. The effects on behaviour were analyzed after 4, 9 and 13 weeks of the experiment. The most manifest behavioural effects were found in rats exposed to the combination, and the changes included increased preening time at the 4th week and increased ambulation and rearing at the end of the exposure. The ethanol ingestion affected also the accumulation of the solvent burden by delaying the peak solvent concentration in the perirenal fat to the 8th week of exposure. The fat solvent concentration did not differ from each other in the two groups at the end of the experiment, and they were similar as compared the concentration found in phenobarbital-pretreated rats exposed for reference. The styrene exposure had almost no effects on cerebral glial cells whereas ethanol induced unexpectedly increased protein destruction in them throughout the experiment. Co-exposure to ethanol and styrene decreased the magnitude of protein destruction in the glial cells. Withdrawal of the rats after an 8-week exposure showed that the styrene effects were largely abolished in two weeks of exposure-free period as analyzed by the determination of brain RNA and acid proteinase activity. Brain RNA was lower than control after two weeks of ethanol deprivation. The present data indicate that marked metabolic interactions between ethanol and styrene take place in agreement with experience on other similar solvent combinations.

Neurochemical and behavioural effects of long-term intermittent inhalation of xylene vapour and simultaneous ethanol intake

Two-month-old male Wistar rats were exposed to 300 p.p.m. of xylene vapour with simultaneous ethanol ingestion for 5 to 18 weeks. Neurochemical effects of mere vapour inhalation included an increase in microsomal superoxide dismutase activity in brain at the end of the experiment. Concomitant ethanol ingestion added significantly to the xylene-induced effects by causing increased proteolysis at the 9th and 14th week of exposure whereas cerebral superoxide dismutase failed to increase in these animals. Preening frequency decreased transiently in ethanol and in xylene groups at 6 and 9 to 12 weeks, respectively, whereas increased ambulation occurred only in the xylene--ethanol group after 12 and 14 weeks of exposure. The behavioural effects were therefore different in the combined exposure, and our biochemical and behavioural observations may point at significant interaction of both solvents although the biochemical mechanisms remain largely unexplained.