Lipid peroxidation and antioxidant enzymes in vanadate-treated rats

Male Wistar rats received an aqueous solution of ammonium metavanadate (AMV) of 0.15 mg/V/ml concentration instead of water for 14 days. The erythrocyte count and haemoglobin level in blood were not changed; the haematocrit index was slightly increased. The spontaneous lipid peroxidation in kidney and liver homogenates was increased. The Fe(II)- or ascorbate-induced lipid peroxidation was more pronounced in the kidney than in the liver. No changes in lipid peroxidation were observed in erythrocytes after AMV treatment. The AMV treatment resulted in a decrease in the activity of the antioxidant enzymes, catalase and glutathione peroxidase in the kidney and liver; the cytosolic Cu,Zn-SOD and mitochondrial Mn-SOD were unchanged. The activity of the enzymes in blood was not changed. The results are discussed with a view to the participation of lipid peroxidation in vanadium toxicity.     

Effects of benzo[a]pyrene on tissue activities of metabolizing enzymes and antioxidant system in normal and protein-malnourished rats

The effects of benzo[a]pyrene (B[a]P) on some drug-metabolizing and antioxidant systems in liver, lung, and stomach were investigated in normal and protein malnutrition (PM) rats. PM significantly inhibited tissue glutathione (GSH) content and increased hepatic lipid peroxidation. Cytochrome P450 isoform CYP1A1 was significantly increased in various tissues (42-73%). Also, lung glutathione S-transferase (GST) activity was significantly decreased (19%) in PM rats. On the other hand, B[a]P significantly induced tissue GSH of control and PM rats. Also, hepatic lipid peroxidation were significantly increased in control rats treated with B[a]P. Superoxide dismutase (SOD) activity was decreased by B[a]P treatment in PM rat stomach. B[a]P significantly induced both quinone reductase (QR) (in all tissues) and hepatic GST of control and PM rats. GST activity in PM rat liver was significantly higher than that of control rat liver after B[a]P treatment. Also, B[a]P induced hepatic CYP1A1 by 32-fold and 27-fold (P < or = 0.05) in control and PM rats, respectively. Stomach and hepatic UDP-glucuronosyltransferase activities were significantly decreased (34%) and increased (74%), respectively by B[a]P in PM rats. The results suggest that PM status has a modifying effect on the response of some antioxidant and metabolizing systems to a well-known carcinogen risk.     

Lipid peroxidation and activity of antioxidant enzymes in diabetic rats

We hypothesized that oxygen free radicals (OFRs) may be involved in pathogenesis of diabetic complications. We therefore investigated the levels of lipid peroxidation by measuring thiobarbituric acid reactive substances (TBARS) and activity of antioxidant enzymes [superoxide dismutase (SOD), glutathione peroxidase (GSH-Px) and catalase (CAT)] in tissues and blood of streptozotocin (STZ)-induced diabetic rats. The animals were divided into two groups: control and diabetic. After 10 weeks (wks) of diabetes the animals were sacrificed and liver, heart, pancreas, kidney and blood were collected for measurement of various biochemical parameters. Diabetes was associated with a significant increase in TBARS in pancreas, heart and blood. The activity of CAT increased in liver, heart and blood but decreased in kidney. GSH-Px activity increased in pancreas and kidney while SOD activity increased in liver, heart and pancreas. Our findings suggest that oxidative stress occurs in diabetic state and that oxidative damage to tissues may be a contributory factor in complications associated with diabetes.     

Xenobiotic-metabolizing enzymes and benzo[a]pyrene metabolism in the benzo[a]pyrene-sensitive mutant strain of Drosophila simulans.

Basal levels of aryl hydrocarbon hydroxylase, epoxide hydrolase and glutathione S-transferase enzyme activities, cytochrome P-450 content and inducibility of enzymes with phenobarbital were found to be similar in the microsomes of D. simulans mutant strain 364yv, which is sensitive to the toxic and mutagenic effects of benzo[a]pyrene (BP), and of the wild resistant Turku strain. In contrast, increases in the rate of BP turnover per molecule of cytochrome P-450, intensity of the hemoprotein band with apparent molecular weight 56,000 and the yield of BP 7,8-dihydrodiol and 9,10-dihydrodiol occurred only in microsomes of BP-pretreated 364yv flies but not of Turku ones. It is likely that BP induces an aberrant form of cytochrome P-450 in 364yv flies with a rare mutation in one of the P-450 regulating genes.     

Metabolism of benzo[a]pyrene VI. Stereoselective metabolism of benzo[a]pyrene and benzo[a]pyrene 7,8-dihydrodiol to diol epoxides

(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-1) and (±)-7β,8α-dihydroxy-9α,10α-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-2) are highly mutagenic diol epoxide diastereomers that are formed during metabolism of the carcinogen (±)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene. Remarkable stereoselectivity has been observed on metabolism of the optically pure (+)- and (?)-enantiomers of the dihydrodiol which are obtained by separation of the diastereomeric diesters with (?)-α-methoxy-α-trifluoromethylphenylacetic acid. The high stereoselectivity in the formation of diol epoxide-1 relative to diol epoxide-2 was observed with liver microsomes from 3-methylcholanthrene-treated rats and with a purified cytochrome P-448-containing monoxygenase system where the (?)-enantiomer produced a diol epoxide-2 to diol epoxide-1 ratio of 6 : 1 and the (+)-enantiomer produced a ratio of 1 : 22. Microsomes from control and phenobarbital-treated rats were less stereospecific in the metabolism of enantiomers of BP 7,8-dihydrodiol. The ratio of diol epoxide-2 to diol epoxide-1 formed from the (?)- and (+)-enantiomers with microsomes from control rats was 2 : 1 and 1 : 6, respectively. Both enantiomers of BP 7,8-dihydrodiol were also metabolized to a phenolic derivative, tentatively identified as 6,7,8-trihydroxy-7,8-dihydrobenzo[a]pyrene, which accounted for ～30% of the total metabolites formed by microsomes from control and phenobarbital-pretreated rats whereas this metabolite represents ～5% of the total metabolites with microsomes from 3-methylcholanthrene-treated rats. With benzo[a]pyrene as substrate, liver microsomes produced the 4,5-, 7,8- and 9,10-dihydrodiol with high optical purity (>85%), and diol epoxides were also formed. Most of the optical activity in the BP 7,8-dihydrodiol was due to metabolism by the monoxygenase system rather than by epoxide hydrase, since hydration of (±)-benzo[a]pyrene 7,8-oxide by liver microsomes produced dihydrodiol which was only 8% optically pure. Thus, the stereospecificity of both the monoxygenase system and, to a lesser extent, epoxide hydrase plays important roles in the metabolic activation of benzo[a]pyrene to carcinogens and mutagens.     

Analysis of benzo[a]pyrene deactivation mechanisms in rats

The experimental data on the effects of a widespread carcinogen, benzo[a]pyrene (BP), on individual reactions of rats were treated using mathematical-statistical methods. The individual reactions were analyzed in dependence of doses and modes of administration (single or chronic). The analysis revealed a statistically significant correlation between life span and urinary content of (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (7,8-BP) in rats treated with BP. The calculated regression equations revealed that the individual sensitivity to carcinogen in case of the BP single administration to rats is mainly determined by efficiency of excretion of the BP active forms out of the organism, whereas after chronic BP administration it is determined by mechanisms of enzymatic deactivation of BP.     

Ellagic acid toxicity and interaction with benzo[a]pyrene and benzo[a]pyrene 7,8-dihydrodiol in human bronchial epithelial cells

Ellagic acid, a plant phenol present in various foods consumed by humans, has been reported to have both anti-mutagenic and anti-carcinogenic potential. To evaluate the potential anti-carcinogenic property of ellagic acid, we tested its effects on the toxicity of ben-zo[a]pyrene and benzo[a]pyrene, 7,8-dihydrodiol and binding of benzo[a]yrene to DNA in cultured human bronchial epithelial cells. The toxicity of ellagic acid itself for human bronchial epithelial cells was also determined. Using a colony-forming efficiency assay, it was found that a nontoxic concentration of ellagic acid (5 g/ml) enhanced the toxicity of benzo[a]pyrene.7,8-dihydrodiol in human bronchial epithelial cells. In contrast, ellagic acid at concentrations of l.5 and 3.0 g/ml inhibited binding of benzo[a]pyrenemetabolites to DNA in these cells. An explanation for the potentiating effect of ellagic acid on the toxicity of benzo[a]pyrene, 7,8-dihydrodiol will require further investigation into the possible mechanisms of interaction between these two compounds.Abbreviations B[a]P benzo[a]pyrene - B[a]P 7,8-DHD (±)trans-7,8-dihydro-7,8-dihydroxybenzo[a]pyrene - B[a]PDE-1 (±)-7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene - B[a]PDE-2 (±) 7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene - B[a]PDE-1:dG N²-]10{7,8,9-dihydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene]yl}:deoxyguanosine - B[a]PDE-2:dG NZ-{10-[7,8,9-trihydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene]yl}:deoxyguanosine - CFE colony forming efficiency - EA ellagic acid - HBE human bronchial epithelial     

Benzo[a]pyrene-DNA-adducts and monooxygenase activities in mice treated with benzo[a]pyrene, cigarette smoke or cigarette smoke condensate

Synchronous fluorescence spectrophotometry (SFS), developed to study benzo[a]pyrene-7,8-diol-9,10-epoxide(BPDE)-DNA, was used to measure the in vivo formation of DNA-adducts in genetically responsive C57BL/6 (B6) and non-responsive DBA/2 (D2) mice. Treatment with cigarette smoke by inhalation for 3-16 days, or i.p. injection of cigarette smoke condensate or neutral fraction did not lead to detectable levels of BPDE-DNA-adducts in either lungs or liver, although aryl hydrocarbon hydroxylase (AHH) activity, an indicator of benzo[a]pyrene (BP) metabolism, was clearly induced in lungs of B6 mouse. A dose-dependent amount of BPDE-DNA-adducts in lung and somewhat less in liver was found after i.p. injection with BP (20-80 mg/kg). Mice treated with vehicle or 4 mg/kg of BP were negative for adducts by SFS. In B6 mice AHH was induced both in lungs and livers while there was no AHH induction in D2 mice although the levels of BPDE-DNA-adducts were somewhat higher than in B6 mice. Thus, no clear correlation seems to exist between AHH activity and the formation of BPDE-DNA-adducts. Also, according to our results SFS can be used to quantitate adduct-formation in in vivo animal studies.     

The oxidation of benzo[a]pyrene mediated by lipid peroxidation in irradiated synthetic diets

The effect of gamma-irradiation (1000-4000 Gy) on the formation of lipid peroxides and on the oxidation of the environmental carcinogen benzo[a]pyrene (BP) has been studied in mixtures of starch/fat and BP which were used as models for natural foods. When mixtures containing polyunsaturated fats (mackerel oil and cod-liver oil which contain relatively large proportions of C20:5 and C22:6) were exposed to gamma-irradiation, large concentrations of lipid peroxide were formed and a concomitant oxidation of BP to mutagenic and toxic BP quinones took place. The rate of BP oxidation was closely related to the extent of peroxidation of the lipids in the starch mixtures and was dependent on the dose of gamma-irradiation and the presence of air. Mackerel oil also underwent peroxidation during the storage of both irradiated and unirradiated starch/mackerel oil/BP mixtures and this resulted in a significant oxidation of the BP present in these samples. Antioxidants such as vitamin E and BHA inhibited both lipid peroxidation and BP oxidation resulting from gamma-irradiation. These results demonstrate that the species generated during the peroxidation of unsaturated fats in foodstuffs can react with polycyclic aromatic hydrocarbons such as BP and convert them into active mutagenic and toxic products. This has important toxicological implications, particularly as the consumption of polyunsaturated fat in the Western world is increasing and gamma-irradiation may soon be widely used for food sterilization.     

Quinone formation from carcinogenic benzo[a]pyrene mediated by lipid peroxidation in phosphatidylcholine liposomes

The behavior of benzo[a]pyrene (B[a]P) during peroxidation of phosphatidylcholine (PC) liposomes initiated by an azo compound was investigated to examine the mechanism of quinone formation from carcinogenic B[a]P mediated by nonenzymatic lipid peroxidation occurring in vivo. B[a]P had a retarding effect on the peroxidation of polyunsaturated fatty acid moiety of PC. The major oxidation products which accumulated in the peroxidized liposomes were B[a]P 1,6-, 3,6-, and 6,12-quinone. Antioxidants acting as scavengers of chain-propagating lipid peroxy radicals effectively prevented not only lipid peroxidation but also B[a]P oxidation in the liposomal suspension. PC hydroperoxides, the primary products of PC oxidation, did not react with B[a]P in the absence of the azo compound, indicating that lipid peroxy radicals, not lipid hydroperoxides, are responsible for the formation of these quinones. The experiments using 18O2 gas and 18O-labeled methyl linoleate hydroperoxides demonstrated that B[a]P quinones are formed by incorporating molecular oxygen and their origin is partly due to the lipid peroxy radical. The mechanism proposed for the formation of B[a]P quinones mediated by peroxidation of membrane lipids involves a direct attack of the lipid peroxy radical on B[a]P and subsequent autocatalytic oxidation. Weak carcinogenic and noncarcinogenic pentacyclic aromatic hydrocarbons showed little reactivity to the lipid peroxy radical in the liposomes. Thus, the facility of the peroxidative attack on B[a]P may be related to the powerful carcinogenic activity of this substance.     

Photolysis primes biodegradation of benzo[a]pyrene

14C-labeled benzo[a]pyrene (BaP) was used as a model-compound for polycyclic aromatic hydrocarbons (PAH) in order to assess the effect of photolytic pretreatment on the subsequent fate of BaP in sewage sludge and soil test systems. Photolysis was performed in methanolic solution with or without 0.1 M H2O2, under either UV light (300 nm) or natural sunlight. The presence of H2O2 greatly enhanced the rate of photolysis both with UV and with natural sunlight. Intact BaP resisted biodegradation in both test systems. Photolysis transformed BaP to polar materials that were subject to increased mineralization and binding in both biological test systems. As shown by the Ames assay, photolysis decreased the mutagenicity of BaP to test strains TA98 and TA104 only moderately. The photolysate had an increased acute toxicity and lost its need for activation by S-9 enzymes. However, during subsequent incubation in soil or sewage sludge, mutagenicity decreased rapidly by one to two orders of magnitude and acute toxicity disappeared due to the mineralization and binding of photoproducts to humic materials. Photolysis of BaP and similar PAH compounds represents a useful treatment option that could be applied to certain PAH-containing petroleum refinery sludge and to coal tar residues in order to facilitate their detoxification and environmentally safe disposal.     

Prevention by N-acetylcysteine of benzo[a]pyrene clastogenicity and DNA adducts in rats

The daily i.t. administration of benzo[a]pyrene (BP) to Sprague-Dawley rats, for 3 consecutive days, did not cause any toxicity or clastogenicity in bone marrow cells, as evaluated by monitoring the ratio of polychromatic to normochromatic erythrocytes and the frequency of micronucleated polychromatic erythrocytes. However, BP produced a considerable enhancement of binucleated and micronucleated pulmonary alveolar macrophages, as well as a significant increase in polymorphonucleates recovered by bronchoalveolar lavage. These effects were prevented by administering the thiol N-acetylcysteine (NAC) by gavage 5 h before each BP instillation. In addition, the i.t. treatment with BP resulted in the formation of BP diolepoxide (BPDE)-DNA adducts in lungs and liver, as assessed by synchronous fluorescence spectrophotometry, with fluorescence peaks of similar magnitude in the 2 tissues. Pretreatment with NAC by gavage completely prevented BPDE adducts to liver DNA and significantly decreased those to lung DNA.     

Indigenous and enhanced mineralization of pyrene, benzo[a]pyrene, and carbazole in soils.

We studied the mineralization of pyrene, carbazole, and benzo[a]pyrene in soils obtained from three abandoned coal gasification plants in southern Illinois. The soils had different histories of past exposure to hydrocarbon contamination and different amounts of total organic carbon, microbial biomass, and microbial activity. Mineralization was measured by using serum bottle radiorespirometry. The levels of indigenous mineralization of 14C-labeled compounds ranged from 10 to 48% for pyrene, from undetectable to 46% for carbazole, and from undetectable to 25% for benzo[a]pyrene following long-term (greater than 180-day) incubations. Pyrene and carbazole were degraded with short or no lag periods in all soils, but benzo[a]pyrene mineralization occurred after a 28-day lag period. Mineralization was not dependent on high levels of microbial biomass and activity in the soils. Bacterial cultures that were capable of degrading pyrene and carbazole were isolated by enrichment, grown in pure culture, and reintroduced into soils. Reintroduction of a pyrene-degrading bacterium enhanced mineralization to a level of 55% within 2 days, compared with a level of 1% for the indigenous population. The carbazole degrader enhanced mineralization to a level of 45% after 7 days in a soil that showed little indigenous carbazole mineralization. The pyrene and carbazole degraders which we isolated were identified as a Mycobacterium sp. and a Xanthamonas sp., respectively. Our results indicated that mineralization of aromatic hydrocarbons can be significantly enhanced by reintroducing isolated polycyclic aromatic hydrocarbon-degrading bacteria.     

Indigenous and enhanced mineralization of pyrene, benzo[a]pyrene, and carbazole in soils.

We studied the mineralization of pyrene, carbazole, and benzo[a]pyrene in soils obtained from three abandoned coal gasification plants in southern Illinois. The soils had different histories of past exposure to hydrocarbon contamination and different amounts of total organic carbon, microbial biomass, and microbial activity. Mineralization was measured by using serum bottle radiorespirometry. The levels of indigenous mineralization of 14C-labeled compounds ranged from 10 to 48% for pyrene, from undetectable to 46% for carbazole, and from undetectable to 25% for benzo[a]pyrene following long-term (greater than 180-day) incubations. Pyrene and carbazole were degraded with short or no lag periods in all soils, but benzo[a]pyrene mineralization occurred after a 28-day lag period. Mineralization was not dependent on high levels of microbial biomass and activity in the soils. Bacterial cultures that were capable of degrading pyrene and carbazole were isolated by enrichment, grown in pure culture, and reintroduced into soils. Reintroduction of a pyrene-degrading bacterium enhanced mineralization to a level of 55% within 2 days, compared with a level of 1% for the indigenous population. The carbazole degrader enhanced mineralization to a level of 45% after 7 days in a soil that showed little indigenous carbazole mineralization. The pyrene and carbazole degraders which we isolated were identified as a Mycobacterium sp. and a Xanthamonas sp., respectively. Our results indicated that mineralization of aromatic hydrocarbons can be significantly enhanced by reintroducing isolated polycyclic aromatic hydrocarbon-degrading bacteria.     

Lipid peroxidation and some antioxidant enzymes in nasal polyp tissue

Nasal polyp (NP) is considered an inflammatory condition in nasal and paranasal sinus cavities and is frequently encountered in otolaryngology clinics. Although the pathophysiology of nasal polyps is poorly understood, it seems likely that the epithelium may play a critical role in the genesis of inflammatory nasal disease. The aim of this study was to investigate the role of free radicals and antioxidant enzymes in NP and compare these findings with concha bullosa (CB). NP and CB were obtained from 27 and 23 patients, respectively. Glutathione peroxidase (GSH-Px), catalase (CAT), xanthine oxidase (XO) total (enzymic plus non-enzymic) superoxide scavenger activity (TSSA), non-enzymic superoxide scavenger activity (NSSA), superoxide dismutase (SOD), and MDA levels in NP and CB were measured. GSH-Px activiy was significantly lower in patients with NP than in the CB group. However, CAT, XO activities and MDA levels were significantly higher in patients with NP than in the CB group, but TSSA, NSSA and SOD activities were unchanged. Increases in the levels of tissue MDA in patients with NP compared to the CB group may indicate the presence of free radical damage in patients with nasal NP.     

锌、苯并[a]芘及其复合胁迫对小麦幼苗生长及抗氧化酶的影响

采用水培方法研究了锌(Zn)、苯并[a]芘(B[a]P)及其复合污染对小麦(Triticum aestivum L.)幼苗生长和超氧化物歧化酶(SOD)、过氧化物酶(POD)活性和过氧化氢酶(CAT)活性的影响.结果表明:与对照组相比,各处理小麦生物量下降,株高降低,300mg·L-1ZnSO4和54mg.L-1B[a]P的复合胁迫使小麦幼苗地上及地下干重分别下降36.4％和51.7％,明显高于单一胁迫.各处理SOD活性呈现升高-降低-升高趋势,且低于对照,POD、CAT活性先升高再降低,复合胁迫POD活性最高,CAT活性最低.Zn、B[a]P及其复合胁迫下,小麦幼苗的生长受到了一定的抑制,且以复合胁迫最为显著.Zn、B[a]P联合作用的结果表现为协同作用.     

Arsenic co-exposure potentiates benzo[a]pyrene genotoxicity

The reactive industrial chemicals acrylamide (AA) and N-methylolacrylamide (MAA) are neurotoxic and carcinogenic in animals, MAA showing a lower potency than AA. The causative agent in AA-induced carcinogenesis is assumed to be the epoxy metabolite, glycidamide (GA), which in contrast to AA gives rise to stable adducts to DNA. The causative agent in MAA induced carcinogenesis is so far not studied. The two AAs were studied in mice and rats using analysis of hemoglobin (Hb) adducts as a measure of in vivo doses and the in vivo micronucleus (MN) assay as an end-point for chromosome damage. Male CBA mice were treated by intraperitoneal (i.p.) injection of three different doses and male Sprague-Dawley rats with one dose of each AA. Identical adducts were monitored from the two AAs [N-(2-carbamoylethyl)valine] and the respective epoxide metabolites [N-(2-carbamoyl-2-hydroxyethyl)valine]. Per unit of administered amount, AA gives rise to higher (three to six times) Hb adduct levels than MAA in mice and rats. Mice exhibit, compared with rats, higher in vivo doses of the epoxy metabolites, indicating that AAs were more efficiently metabolized in the mice. In mouse the two AAs induced dose-dependent increases in both Hb adduct level and MN frequency in peripheral erythrocytes. Per unit of administered dose MAA showed only half the potency for inducing micronuclei compared with AA, although the MN frequency per unit of in vivo dose of measured epoxy metabolite was three times higher for MAA than for AA. No increase in MN frequency was observed in rat bone marrow erythrocytes, after treatment with either AA. This is compatible with a lower sensitivity of the rat than of the mouse to the carcinogenic action of these compounds.     

An analysis of DNA replication in synchronized CHO cells treated with benzo[a]pyrene diol epoxide

Synchronized Chinese hamster ovary (CHO) cells treated with (+/-)7 beta,8 alpha- dihydroxy-9 alpha,10 alpha-epoxy-7,8,9,10-dihydrobenzo[a]pyrene (BP diol epoxide I) were used to test the 'block-gap' model of replicative bypass repair in mammalian cells. One feature of the model is that carcinogenic or mutagenic DNA adducts act as blocks to the DNA replication fork on the leading strand. Using synchronized CHO cells, the rate of S phase progression by BrdUrd labeling of newly replicated DNA was measured. The rate of S phase progression was reduced by 22% and 42%, when the cells were treated at the G1/S boundary with 0.33 and 0.66 microM BP diol epoxide I, respectively. Using the pH step alkaline elution assay, it was found that the reduced rate of S phase progression was due to a delay in the appearance of multiple replicon size nascent DNA. This observation was consistent with the frequency of BP-DNA adducts present in the leading strand. A second feature of the 'block-gap' model is that the adduct-induced blockage on the lagging strand will produce gaps. It was determined by the use of high-resolution agarose gel electrophoresis, that the ligation of Okazaki size replication intermediates was blocked in a dose-dependent manner in BP diol epoxide I treated, synchronized CHO cells. These data are consistent with a block to the leading strand of DNA replication at DNA-carcinogen adducts. An inhibition of the ligation of Okazaki size fragments by BP diol epoxide I implies a block to replication of the DNA lagging strand leading to gap formation. The data presented here are, therefore, supportive of the 'block-gap' model of replicative bypass repair in carcinogen damaged mammalian cells.