Prostaglandins and their precursors can modify genetic damage-induced by gamma-radiation and benzo(a)pyrene

Experiments were performed to study the effect of various prostaglandins (PGs) and their precursors, gamma-linolenic acid (GLA) and arachidonic acid (AA) on gamma-radiation and benzo (a) pyrene (BP)-induced genetic damage to the bone marrow cells of mice, using the sensitive micronucleus (MN) test. Thromboxane B2 prostaglandin E1 and GLA completely prevented BP-induced and reduced to a great degree radiation-induced genetic damage, where as PGE2, PGF2 alpha and AA were without any effect. Since GLA and AA are widely distributed in the cell membranes, and as PGs can be formed virtually in response to any type of stimulus, it is likely that GLA and PGE1 may function as endogenous anti-mutagenic chemicals.     

Prostaglandins and their precursors can modify genetic damage-induced by gamma-radiation and benzo (a) pyrene

Experiments were performed to study the effect of various prostaglandins (PGs) and their precursors, gamma-linolenic acid (GLA) and arachidonic acid (AA) on gamma-radiation and benzo (a) pyrene (BP) -induced genetic damage to the bone marrow cells of mice, using the sensitive micronucleus (MN) test. Thromboxane B2 prostaglandin E1 and GLA completely prevented BP-induced and reduced to a great degree radiation-induced genetic damage. where as PGE2, PGF2alpha and AA were without any effect. Since GLA and AA are widely distributed in the cell membranes, and as PGs can be formed virtually in response to any type of stimulus., it is likely that GLA and PGE1 may function as endogenous anti-mutagenic chemicals.     

乳杆菌吸附苯并芘的特性

[目的]探讨植物乳杆菌(Lactobacillus plantarum)121和戊糖乳杆菌(Lactobacillus pentosus)ML32的苯并芘吸附作用与机制.[方法]采用高效液相色谱检测菌体对苯并芘的吸附率.[结果]菌株121和ML32对苯并芘的吸附率分别为65.9%和64.9%,这种吸附特性与菌体活力无关,随培养时间延长、温度提高以及细胞浓度的上升而增加.菌株121和ML32的吸附率在pH 4和5时达到最大,分别为87.6%和89.0%.当培养液中Ca2+或Mg2+浓度大于0.05mol/L时,菌体吸附率与盐离子浓度呈正相关.苯洗脱会导致乳杆菌所吸附的苯并芘减少90%.经碱性蛋白酶、中性蛋白酶、溶菌酶及TCA和SDS等方法处理后,菌体吸附率上升,且不易被苯去除.在胆盐及胃酸环境下,两株菌的吸附率均提高至70%以上,而胰蛋白酶的存在仅对菌株121的吸附率有较大影响.[结论]两株乳杆菌可以通过吸附作用从环境中清除苯并芘,其吸附效果与细菌细胞壁的结构和组成有关.     

Reactivity with DNA of three pyrenofuran analogues of benzo(a)pyrene and benzo(e)pyrene

Three pyrenofurans, the pyreno[1,2-b]furan (FP1), the pyreno[2,1-b] furan (FP2) and the pyreno[4,5-b]furan (FP3) have been synthesized as analogues of the mutagenic and carcinogenic benzo(a)pyrene (FP1 and FP2) and of its non-carcinogenic isomer benzo(e)pyrene (FP3). For each of the pyrenofurans, the reactivity with DNA has been tested in presence of liver microsomes of rats induced with 3-methylcholanthrene. Fluorescence spectroscopy showed that only FP2 and FP3 which possess a "bay region" react with DNA. In both cases, metabolites bound to DNA have a fluorescence emission comparable to that of the "bay region" dihydrodiols obtained after the "in vitro" metabolism of initial molecules. FP2 is shown to react similarly to benzo(a)pyrene whereas the reactivity of FP3 is different from that of benzo(e)pyrene, in spite of their structural similarities. This is probably due to reasons of three-dimensional space configuration. The peculiar reactivity of FP3 is predicted by calculations of the bond order values.     

Benzo(a)pyrene activates L1Md retrotransposon and inhibits DNA repair in vascular smooth muscle cells

Benzo(a)pyrene (BaP) modulates vascular smooth muscle cells (vSMCs) from a quiescent to proliferative phenotype, a shift associated with activation of L1Md retrotransposon [K.P. Lu, K.S. Ramos, Biochem. Biophys. Res. Commun. 253 (1998) 828-833]. The present studies were conducted to evaluate L1Md activation profiles in murine vSMCs treated with BaP or its oxidative metabolites, and to screen for possible insertional mutations into p53 and retinoblastoma (RB) genes. We also sought to examine the profile of DNA damage and repair in BaP-treated vSMCs. Northern analysis revealed that BaP (0. 03-3microM), and its major reactive 7,8-diol metabolite (0. 03-3microM), activate L1Md gene in a concentration-dependent manner. Two other metabolites, 3-OH BaP and 3,6-BaP quinone (0.03-3microM), as well as hydrogen peroxide (25-75microM) also activated L1Md. No insertional mutations into either p53 or RB genes were observed in vSMCs treated with BaP in vitro, although a slight elevation of p53 mRNA was observed as early as 4h after chemical challenge. Treatment of vSMCs with 3 or 30microM BaP for 4h increased unscheduled DNA synthesis (UDS) 1.4- and 2.5-fold, respectively. Challenge with 0. 3microM BaP for 24h inhibited DNA repair capacity in vSMCs for up to 48h. These results demonstrate that BaP and its oxidative metabolites activate L1Md retrotransposon in vSMCs, which coupled to DNA damage and inhibition of DNA repair are part of the atherogenic response elicited by BaP and related hydrocarbons.     

Metabolism of benzo(a)pyrene by duck liver microsomes

The metabolism of benzo(a)pyrene [BP], a model carcinogenic PAH, by hepatic microsomes of two duck species, mallard (Anas platyrhynchos) and common merganser (Mergus merganser americanus) collected from chemically-contaminated and relatively non-contaminated areas was investigated. The rate of metabolism of BP by liver microsomes of common merganser and mallard collected from polluted areas (2,650 +/- 310 and 2,200 +/- 310 pmol/min per mg microsomal protein, respectively) was significantly higher than that obtained with liver microsomes of the two species collected from non-polluted areas (334 +/- 33 and 231 +/- 30 pmol/min per mg microsomal protein, respectively). The level of cytochrome P-450 1A1 was significantly higher in the liver microsomes of both duck species from the polluted areas as compared to the ducks from the non-polluted areas. The major BP metabolites, including BP-9, 10-diol, BP-4, 5-diol, BP-7, 8-diol, BP-1, 6-dione, BP-3, 6-dione, BP-6, 12-dione, 9-hydroxy-BP and 3-hydroxy-BP, formed by liver microsomes of both duck species from polluted and non-polluted areas, were qualitatively similar. However, the patterns of these metabolites were considerably different from each other. Liver microsomes of ducks from the polluted areas produced a higher proportion of benzo-ring dihydrodiols than the liver microsomes of ducks from the non-polluted areas, which converted a greater proportion of BP to BP-phenols. The predominant enantiomer of BP-7,8-diol formed by hepatic microsomes of the two duck species had an (-)R,R absolute stereochemistry. The data suggest that duck and rat liver microsomal enzymes have different regioselectivity but similar stereoselectivity in the metabolism of BP.     

Some properties of vicinal diol-epoxides derived from benzo(a)anthracene and benzo(a)pyrene

The alkylating properties of pairs of syn- and anti-isomers of 2 diol-epoxides derived from benzo(a)pyrene (BP) and of 1 derived from benz(a)anthracene (BA) have been investigated. Of the anti-diol-epoxides, anti-BP 7,8-diol-9,10-oxide was the most reactive compound towards DNA, towards sodium p-nitrothiophenolate in a non-aqueous solvent system, and towards 4-(p-nitrobenzyl)pyridine in aqueous solution; anti-BP 9,10,-diol-7,8-oxide was of intermediate reactivity and anti-BA 8,9-diol-10,11-oxide was least reactive. The syn-diol-epoxides gave unsatisfactory results with DNA and 4-(p-nitrobenzyl)pyridine because of their rapid solvolysis in aqueous solution, but with sodium p-nitrothiophenolate showed the order of reactivity syn-BP 7,8-diol-9,10-oxide greater than syn-BA 8,9-diol-10,11-oxide greater than syn-BP 9,10-diol-7,8-oxide. The products of the reaction between diol-epoxides and nucleic acids were examined by Sephadex LH-20 chromatography followed by high-pressure liquid chromatography (HPLC) and the diol-epoxides were shown to react principally with the guanosine and adenosine moieties of RNA.     

Oxidation of benzo(a)pyrene and 7,8-dihydro-7,8-dihydroxy benzo(a)pyrene by horseradish peroxidase-H2O2 intermediate: fluorometric study

The capacity of oxidation of benzo(a)pyrene (BP) and its analog to be oxidized by peroxidases in several tissues has been studied. The kinetics of the horseradish peroxidase (HRP) oxidation of BP and 7,8-dihydro-7,8-dihydroxy benzo(a)pyrene (BP-7,8-diol) were examined. Effective ratios of H2O2 and HRP for catalytic oxidation were 13.74 for BP and 4.58 for BP-7,8-diol. The maximum ratio was approximately 90 for both hydrogen donors (BP and BP-7,8-diol) to the ES complex. The maximum ratio of oxidized BP and BP-7,8-diol to HRP was 5.7. Ks values for H2O2 were 1.68 and 6.35 microM for BP and BP-7,8-diol, respectively. The mean values of the rate constants, k5, for the oxidation of BP and BP-7,8-diol were 0.56 X 10(5) M-1 sec-1 and 4.1 X 10(5) M-1 sec-1, respectively, at low concentrations. At low concentrations a Hill plot of the oxidation of BP showed a negative value (nH = 0.5) and at high concentrations nH = 1.0. On the other hand, that of BP-7,8-diol showed positive cooperativeness (nH = 1.8). These oxidation reactions caused substrate (donor) inhibition at high concentrations. The inhibition constants, KA', were 9.8 and 5.65 microM for BP and BP-7,8-diol, respectively. The reactivity of the oxidation of BP-7,8-diol was five to six times larger than that of BP.     

Metabolic activation of benzo(a)pyrene by human amniotic fluid

The in vitro activation of benzo(a)pyrene was studied in amniotic fluid from ten 4-month pregnant women. Benzo(a)pyrene monooxygenase and epoxide hydrolase activities were in the same range in amniotic fluid as in human liver. Glutathione epoxide transferase activity was markedly lower than in hepatocytes. Human amniotic fluid also catalyzed the formation of hydrocarbon metabolites mutagenic to Salmonella typhimurium TA98 (Ames system). Profiles of amniotic fluid aromatic hydrocarbons from non smokers exhibited low benzo(a)pyrene concentration (less than 0.1 ng/ml).     

Metabolism of benzo(a)pyrene by human lung microsomal fractions

The metabolism of benzo(a)pyrene was studied using microsomal fractions obtained from human lung derived at either resection or autopsy. The rates of metabolism and metabolite distribution were monitored using high pressure liquid chromatography and the metabolic rates were noted to be similar to those obtained using rat lung microsomes. In contrast to the rat, human lung microsomes appear to form a higher percentage of the 7,8-dihydro-7, 8-diol or 9,10-dihydro-9, 10-diol of benzo(a)pyrene as a fraction of the total metabolites. However, there was a significant variation among the human lung microsomal preparations which might reflect the clinical diagnosis and/or individual variation.     

Reduction of benzo(a)pyrene induced chromosomal aberrations by DL-alpha-tocopherol

The antioxidant, DL-alpha-tocopherol (vitamin E), has been demonstrated to significantly reduce the percentage of benzo(a)pyrene (BP) induced chromosomal aberrations in vitro. Chinese hamster lung (Don) and Chinese hamster ovary (CHO) cells were treated with either 1 microgram/ml or 5 micrograms/ml BP for 4 to 28 h; some cultures were treated with S9 mix activated BP. Additional cultures of Don and CHO were treated simultaneously with 100 micrograms/ml of DL-alpha-tocopherol and BP. In CHO cells 1 microgram/ml non-activated BP significantly increased the chromosomal aberration percentage above the control level. Aberrations observed included breaks, gaps, fusions, rings, dicentrics, and polyploids. Chinese hamster Don cells treated with 1 microgram/ml or 5 micrograms/ml S9 mix activated BP contained significant increases in aberration percentages above the control levels. When Don cells were treated simultaneously with activated BP and DL-alpha-tocopherol for 4 h, there was a slight decrease in the total aberration frequency to less than that of cells treated with activated BP only; however, when Don cells were treated with BP and DL-alpha-tocopherol for 28 h, there was a significant reduction in the aberration percentage below that of BP-treated cells alone. Similar results have been obtained with CHO cells treated with nonactivated BP and DL-alpha-tocopherol. The results reported here provide further evidence that antioxidants may prevent the potential mutagenic and carcinogenic effects of certain polycyclic compounds.     

Biodegradation of benzo(a)pyrene by a newly isolated Fusarium sp

Benzo(a)pyrene (BaP) is a five-ring polycyclic aromatic hydrocarbon produced by the incomplete combustion of organic materials. It is one of the priority pollutants listed by the US Environmental Protection Agency. This study describes a fungal isolate that is able to biodegrade benzo(a)pyrene. The filamentous fungus, isolated from leaves of Pterocarpus macrocarpus Kurz., was identified as a Fusarium sp. (strain E033). Fusarium sp. E033 was able to survive in the presence of benzo(a)pyrene concentrations up to 1.2 mM (300 mg L(-1)). Biodegradation experiments using 0.4 mM (100 mg L(-1)) benzo(a)pyrene demonstrated that Fusarium sp. E033 was able to degrade 65-70% of the initial benzo(a)pyrene provided, and two transformation products, a dihydroxy dihydro-benzo(a)pyrene and a benzo(a)pyrene-quinone, were detected within 30 days of incubation at 32 degrees C. The factors affecting biodegradation efficiency were also investigated. While increasing aeration promoted better fungal growth and benzo(a)pyrene biodegradation, increasing the glucose concentration from 5 to 50 mM had an adverse effect on biodegradation. Ethanol and methanol, provided at 5 mM to increase benzo(a)pyrene water solubility, increased the fungal biomass yield but did not promote degradation. The Fusarium sp. E033 isolated in this study can tolerate and degrade relatively high concentrations of benzo(a)pyrene, suggesting its potential application in benzo(a)pyrene bioremediation.     

Metabolism of benzo(a)pyrene,dimethylbenzanthracene and aflatoxin B1 by camel liver microsomes

The ability of camel liver microsomes to metabolise a range of common environmental carcinogens including benzo(a)pyrene, dimethylbenzanthracene and aflatoxin B1 has been investigated. The camel liver has shown the ability to metabolise benzo(a)pyrene, dimethylbenzanthracene and aflatoxin B1 to a number of metabolites. The major metabolites of benzo(a)pyrene produced by camel liver enzymes were identified as its mono-hydroxy derivatives and suggest that the metabolic detoxification pathways of carcinogen metabolism are predominant in this species. Benzo(a)pyrene metabolising activity in camel liver required NADPH and was inhibited by CO and alpha-naphthoflavone suggesting the involvement of cytochrome P450 in the metabolism of this carcinogen by camel liver. The cytochrome P450-dependent metabolism of carcinogen and other specific substrates such as ethoxyresorufin and ethoxycoumarin, by camel liver enzymes, was about 50% higher than that of rat liver enzymes. The cytochrome P450-dependent metabolism of a variety of carcinogenic and other substrates by camel liver demonstrated that there are multiple forms of cytochrome P450 enzymes involved in the metabolism of a wide array of xenobiotics and pollutants.     

Metabolism of benzo(a)pyrene by isolated hepatocytes and factors affecting covalent binding of benzo(a)pyrene metabolites to DNA in hepatocyte and microsomal systems

Covalent binding of benzo(a)pyrene (BP) metabolites to DNA was investigated in hepatocytes and liver microsomes (MC-microsomes) isolated from 3-methylcholanthrene-treated rats. The major DNA adducts formed during BP metabolism in both hepatocytes and incubations of calf thymus DNA with MC-microsomes were adducts of anti and syn isomers of trans-7,8,-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene (diol-epoxides) and of epoxide derivatives of BP-9-phenol (phenol-oxides). Diol-epoxide adducts predominated over phenol-oxide adducts in hepatocytes, while the reverse was found in microsomal incubations. In hepatocytes, both diol-epoxide and phenol-oxide adducts increased with increasing BP concentration; the ratio of diol-epoxide adduct to phenol-oxide adduct decreased from 6:1 to 3:1 between 30 and 100 μm BP. In microsomal incubations, decreases in DNA concentration or addition of the hepatocyte L15 medium produced larger decreases in phenol-oxide adducts than in diol-epoxide adducts. The effects of the inhibitors salicylamide, diethylmaleate, and 3,3,3,-trichloropropene oxide on formation of BP-DNA adducts are interpreted in terms of changes in precursor formation and metabolism and reductions in hepatocyte glutathione levels. Addition of 1.5 mg/ml exogenous DNA to hepatocyte incubations produced no change in covalent binding to cellular DNA, even though extracellular BP-DNA adducts accounted for 97% of the total adducts formed. Both the relative amounts of diol-epoxide and phenol-oxide adducts and the total adducts per milligram of DNA were indistinguishable with respect to extracellular and intracellular DNA. Modification of extracellular DNA by diol-epoxides was at least as efficient as modification of calf thymus DNA in incubations with MC-microsomes. It is concluded that BP diol-epoxides and phenol-oxides can leave the cell or enter the nucleus with equal facility but are more effective in binding to DNA in the cell in which they are generated.     

Bovine endothelial cells transformed in vitro by benzo(a)pyrene

A cloned strain of bovine vascular endothelial cells with a finite in vitro lifespan was treated with benzo(a)pyrene (BP) after approximately 75% of its lifespan was completed. Untreated cultures of this strain senesced upon serial subcultivation and contained large, nondividing cells. In three out of seven trials, BP treatment produced transformed cells appeared in the cultures concomitant with the senescence of the parent cells. All transformed cell lines examined exhibited indefinite lifespans and altered karyotypes. Two of the lines retained most of the characteristics of normal endothelial cells, except that one became aneuploid and the other polyploid, Neither of these lines formed tumors when inoculated into nude mice. The remaining two lines retained mostly diploid kayotypes, but a high percentage of cells contained Robertsonian translocations. In one line cell volume was markedly reduced. In addition, these lines grew in multilayers, were anchorage independent, and proliferated in medium containing 0.5% serum. When 10⁷ cells of these lines were injected into nude mice, tumors appeared within 1 week and were identified as malignant hemangioendotheliomas of bovine origin.     

Benzo(a)pyrene diolepoxide-haemoglobin and albumin adducts at low levels of benzo(a)pyrene exposure

A biomonitoring study was conducted to simultaneously measure individual benzo(a)pyrene (BaP) exposure in 50 office employees, not occupationally exposed to polycyclic aromatic hydrocarbons (PAH), using personal samplers and the formation of (+) r-7, t-8-dihyroxy-t-9,t-10-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene (BPDE) adducts to haemoglobin (BPDE-Hb) and serum albumin (BPDE-SA). The population enrolled was exposed to an average of 0.58 ± 0.46 ng BaP m^-3 (mean ± SD). The concentration of BaP collected from smokers' samples was double that from non-smokers (P = 0.007). BPDE adducts to Hb and SA were quantified as BaP tetrols released from hydrolysis of macromolecules and measured by high-resolution gas chromatography-negative ion chemical ionization-mass spectrometry. BPDE-Hb adducts were detected in 16% of the population and BPDE-SA adducts in 28%. Smoking did not affect adduct formation. When BaP personal monitoring data were used as the criterion of exposure, no correlation was found with the presence and the levels of BPDE-Hb and BPDE-SA adducts. Undetected sources of PAH, such as the diet, might markedly alter the exposure profile depicted by individual air sampling and affect the frequency and levels of protein biomarkers. This is the first comparative analysis of BPDE-Hb and BPDE-SA adducts, providing reference values for these biomarkers in a general urban population. However it is difficult to establish which biomarkers would be the more relevant in assessing low BaP exposure, due to undetectable factors such as dietary PAHs, that might have influenced the results to some degree.