Genotoxic activity of two furan analogues of benzo[a]pyrene and their 2-nitro derivatives

We measured the genotoxic activities in two bacterial tests, the Salmonella/histidine assay (a reverse mutation assay) and the SOS Chromotest (an assay for SOS induction in E. coli), of two pairs of isomeric furan analogues of benzo[a]pyrene: pyreno[1,2-b]furan (R7490) and pyreno[2,1-b]furan (R7692) and their 2-nitro derivatives, 8-nitro-pyreno[1,2-b]furan (R7489) and 8-nitro-pyreno[2,1-b]furan (R7691). We found that: For all 4 compounds, the responses were correlated in the two tests. For the 2-nitro derivatives, R7489 and R7691, the responses were extremely high, reaching SOS-inducing potencies of 5.2 X 10(3) and 10(5)/nmole in the SOS Chromotest and mutagenic potencies of 6.3 X 10(4) and 3.7 X 10(7) revertants/nmole in the Salmonella/histidine assay (strain TA98), respectively; the responses were only slightly decreased in nitroreductase-deficient strains. The responses to the two pyrenofurans were increased in the presence of an "activating mixture" but were still lower than that to benzo[a]pyrene. In contrast to benzo[a]pyrene and pyreno[2,1-b]furan (R7692), pyreno[1,2-b]furan (R7490) also gave a response in the absence of an "activating mixture". (5) Compounds with the oxygen heteroatom within the "bay region" gave lower responses than their isomers with the oxygen heteroatom outside the "bay region".     

Inhibition of binding of benzo(a)pyrene to DNA by 7,8-benzoflavone in organ cultures of human bronchus

Levels of binding of exogeneously added benzo(a)pyrene to DNA in organ culture were examined in nine specimens of normal human bronchus obtained by bronchoscopy of tumor patients. The specimens were divided into two portions and incubated with [3H]benzo(a)pyrene in the absence or presence of 2 microM 7,8-benzoflavone for 24 h. 7,8-benzoflavone inhibited [3H]benzo(a)pyrene-DNA binding from 24 to 60%. Generally, the levels of binding of [3H]benzo(a)pyrene to DNA in the presence of 7,8-benzoflavone were relatively low and closely bracketed the mean value for the nine specimens. This appears to indicate that there are at least two components to [3H]benzo(a)pyrene-DNA binding catalyzed by the human bronchus. One component is quite variable in activity and is sensitive to inhibition by 7,8-benzoflavone, and may be an environmentally induced activity. The second component is lower in activity, and may be a constitutive portion of the mixed-function oxidase.     

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.     

Free radicals derived from benzo[a]pyrene.

At least four different free radicals can be formed from benzo[a]pyrene under different reaction conditions, namely the 6-oxybenzo[a]pyrene radical, the benzo[a]pyrene anion and cation radicals and a radical from heated benzo[a]pyrene. The formation and esr spectra of these radicals have been studied with the aim of clarifying the nature of the radical species involved under different reaction conditions. Additionally the reactivity of the 6-oxybenzo[a]pyrene and the benzo[a]pyrene cation radicals towards several phenolic antioxidants have also been investigated.     

Detection of benzo(a)pyrene photodegradation products using DNA electrochemical sensors

The reactivity of photodegradation products of benzo(a)pyrene vs. DNA has been assessed using both genomic and oligonucleotide based DNA electrochemical sensors. The kinetic of a photooxidation reaction of benzo(a)pyrene (BaP) carried out in controlled conditions using a 6 W UV lamp peaked at 365 nm has been studied using LC with fluorimetric detection. Degradation of benzo(a)pyrene by both UV and UV/H(2)O(2) exhibited pseudo-first-order reaction kinetics with half-lives ranging from 3.0 to 9.8h depending on the pH and on the amount of H(2)O(2). The oxidation products of benzo(a)pyrene obtained in different conditions were tested on genomic ssDNA electrochemical sensors obtained via immobilisation of salmon testis ss-DNA on graphite screen-printed electrodes. Guanines oxidation signals obtained using chronopotentiometry were used to detect the interaction of the products with DNA. The dose-response curve obtained with benzo(a)pyrene incubated 24 h at pH 4.7 was different from that of the parent compound indicating a different type of interaction with DNA. A DNA hybridisation sensor was also assembled using a thiolated/biotynilated 24-mer oligonucleotide immobilised on a gold screen-printed electrode and avidin-alkaline phosphatase conjugate. A voltammetric detection of naphtol was used to detect the hybridisation reaction. A net inhibition of the hybridisation reaction was observed after incubation with benzo(a)pyrene oxidation products that was attributed to the formation of stable adducts with the guanines of the biotinylated strand. LC-MS-MS studies of the oxidation products confirmed the presence of chemical species potentially forming adducts with DNA. The data reported demonstrate that DNA electrochemical sensors have the potential to be used to monitor remediation processes and to assess the potential toxicity vs. DNA of chemicals forming stable DNA adducts.     

Time course of metabolism of benzo[e]pyrene by hamster embryo cells and the effect of chemical modifiers

In cultures of hamster embryo cells, benzo[a]pyrene (B[a]P) is metabolized primarily in the bay region. In contrast, little or no bay region metabolism of the noncarcinogenic isomer benzo[e]pyrene (B[e]P) could be detected during 12–96-h incubations of hamster embryo cells with 4 μM [³H]B[e]P. The upper limit to 9,10-dihydro-9,10-dihydroxy-B[e]P formation is about 0.2% of the ethyl acetate-soluble metabolites ( <0.1% of the total metabolites). The major identified metabolites of B[e]P were 4,5-dihydro-4,5-dihydroxy B[e]P and the glucuronide conjugates of 3-OH-B[e]P and 4,5-dihydro-4,5-dihydroxy B[e]P. Simultaneous treatment of cells with either B[a]P or 7,8-benzoflavone (BF) did not induce bay region metabolism of [³H]B[e]P.     

Characteristics of binding and transport of benzo(a)pyrene by blood serum lipoproteins

Binding and distribution of 3H-benzo[a]pyrene in lipoprotein fraction of rat blood serum were studied. The binding was enhanced in the row: LDL, VLDL, HDL, Kd lipoprotein-benzo[a]pyrene complexes had been calculated by means of tryptophan fluorescence quenching. It was found, that Kd value benzo[a]pyrene complexes with VLD was 1.5 x 10(-6) M, with LDL -6.6 x 10(-7) M and with HDL -4.2 x 10(-6) M. Radiolabeled benzo[a]pyrene uptake by rat organs and tissues was investigated after i.v. injection of benzo[a]pyrene-complexes with LP of different classes. High uptake activity was revealed for liver, adrenals and kidneys, whereas heart, spleen, thymus were characterized by low 3H-benzo[a]pyrene accumulation. Radioactivity distribution pattern was depended on the class of LP used for complexation. Ours data permit to evaluate the participation of lipoproteins in transport and metabolic pathways of xenobiotics in organism.     

The conversion of benzo(alpha)pyrene 4,5-oxide into 4-hydroxybenzo(alpha)pyrene in the presence of polyriboguanylic acid.

Incubation of benzo[alpha] pyrene 4,5-oxide with poly(G) in neutral aqueous ethanol resulted in the formation of covalent adducts and in the production of free 4-hydroxybenzo[alpha]pyrene. This phenol, which was identified by its UV spectral properties and by its chromatographic characteristics, was also formed but at a much slower rate when the epoxide was incubated with DNA or with GMP. Phenol formation was not detected when benzo[alpha]-pyrene 4,5-oxide was incubated for prolonged periods in the presence of poly(A), poly(C) or poly(U) or in the absence of nucleic acid. Formation of 4-hydroxybenzo[alpha] pyrene from the epoxide in the presence of poly(G) was not accompanied by detectable base modifications or by breakage of phosphodiester linkages.     

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.     

Covalent binding of benzo[a]pyrene to dna in fish liver

Benzo[a]pyrene became bound to the hepatic DNA in juvenile English sole ($\text{Parophrys vetulus}$) force fed tritiated benzo[a]pyrene. No statistically signïficant change was observed in the level of the binding from 16 h to 2 wk after the single exposure. Specific activities of binding were similar for both DNA and protein. Moreover, a binding index was calculated to represent the number of benzo[a]pyrene molecules bound per 10⁶ nucleotides after administration of a theoretical dose of 1 mmole of hydrocarbon per kg body weight. The value for English sole liver DNA was of the same order of magnitude as the values reported for mouse skin and mammary gland in which benzo[a]pyrene is carcinogenic.     

Rapid mineralization of benzo[a]pyrene by a microbial consortium growing on diesel fuel

A microbial consortium which rapidly mineralized the environmentally persistent pollutant benzo[a]pyrene was recovered from soil. The consortium cometabolically converted [7-(14)C]benzo[a]pyrene to (14)CO(2) when it was grown on diesel fuel, and the extent of benzo[a]pyrene mineralization was dependent on both diesel fuel and benzo[a]pyrene concentrations. Addition of diesel fuel at concentrations ranging from 0.007 to 0.2% (wt/vol) stimulated the mineralization of 10 mg of benzo[a]pyrene per liter 33 to 65% during a 2-week incubation period. When the benzo[a]pyrene concentration was 10 to 100 mg liter(-1) and the diesel fuel concentration was 0.1% (wt/vol), an inoculum containing 1 mg of cell protein per liter (small inoculum) resulted in mineralization of up to 17.2 mg of benzo[a]pyrene per liter in 16 days. This corresponded to 35% of the added radiolabel when the concentration of benzo[a]pyrene was 50 mg liter(-1). A radiocarbon mass balance analysis recovered 25% of the added benzo[a]pyrene solubilized in the culture suspension prior to mineralization. Populations growing on diesel fuel most likely promoted emulsification of benzo[a]pyrene through the production of surface-active compounds. The consortium was also analyzed by PCR-denaturing gradient gel electrophoresis of 16S rRNA gene fragments, and 12 dominant bands, representing different sequence types, were detected during a 19-day incubation period. The onset of benzo[a]pyrene mineralization was compared to changes in the consortium community structure and was found to correlate with the emergence of at least four sequence types. DNA from 10 sequence types were successfully purified and sequenced, and that data revealed that eight of the consortium members were related to the class Proteobacteria but that the consortium also included members which were related to the genera Mycobacterium and Sphingobacterium.     

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     

Liver microsomal DT diaphorase: noninvolvement in hydroxylation of benzo(a)pyrene.

A highly purified reconstituted system isolated from the microsomes of 3-methylcholanthrene-treated rats consisting of cytochrome P-448, NADPH-cytochrome $\text{c}$ reductase and synthetic dilauroyl phosphatidylcholine had no DT diaphorase activity, but hydroxylated benzo[a]pyrene at a faster rate than microsomes from 3-methylcholanthrene-treated rats. DT diaphorase purified from liver microsomes of 3-methylcholanthrene-treated rats when added to this reconstituted system did not stimulate or inhibit benzo[a]pyrene hydroxylation, nor could it replace or NADPH-cytochrome $\text{c}$ reductase in supporting the reaction. We therefore conclude that microsomal DT diaphorase is not involved in microsomal hydroxylation of benzo[a]pyrene to its phenolic products despite the observation that both DT diaphorase activity and the hydroxylation of benzo[a]pyrene are induced by 3-methylcholanthrene and 2,3,7,8-tetrachlorodibenzo-$\text{p}$-dioxin     

Induction of fatty acid cyclooxygenase activity in canine kidney cells (MDCK) by benzo(a)pyrene.

Canine kidney cells (MDCK) in which [3H]arachidonic acid was esterified in the cellular lipids released increased levels of radioactive prostaglandins and arachidonic acid into the medium when cultured in the presence of benzo(a)pyrene. When MDCK cells were cultured in the presence of benzo(alpha)pyrene and 7,8-benzoflavone, this increased release was not observed. MDCK cells incubated with benzo(a)pyrene also converted exogenous arachidonic acid into prostaglandins more effectively than cells grown in its absence. 7,8-Benzoflavone inhibited this benzo(a)pyrene effect. Microsomes, prepared from benzo(alpha)pyrene-treated MDCK cells synthesized prostaglandin F2alpha from arachidonic acid more effectively than nontreated cells.     

Dual-label high-performance liquid chromatographic assay for femtomole levels of benzo[a]pyrene metabolites

A dual-label HPLC assay to measure femtomole quantities of ethyl acetate-extractable [3H]benzo[a]pyrene metabolites was developed. 14C-labeled metabolites of benzo[a]pyrene formed by rat liver 9000g supernatant were used as both internal standards and chromatographic markers. The percentage deviation between assays was determined to be between 11 and 13% for 9,10-dihydro-9,10-dihydroxybenzo[a]pyrene, 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene, benzo[a]pyrene-3,6-quinone, benzo[a]pyrene-1,6-quinone, and 9-hydroxybenzo[a]pyrene, 22% for 4,5-dihydro-4,5-dihydroxybenzo[a]pyrene, and less than 5% for 3-hydroxybenzo[a]pyrene. The detection limit of this assay was between 3 and 10 fmol per metabolite. The application of this technique to the metabolism of [3H]benzo[a]pyrene by microsomes of hamster and human oral cavity tissue is described.     

The homogeneity of rat liver microsomal cytochrome P-448 activity and its role in the activation of benzo[a]pyrene to mutagens

The O-deethylation of ethoxyresorufin and the metabolic activation of benzo[a]pyrene to mutagens were determined in hepatic microsomal preparations from control and induced animals. An excellent direct correlation (r = 0.95) has been observed between ethoxyresorufin O-deethylase and the metabolic activation of benzo[a]pyrene to mutagens when the fraction of cytochromes P-450 present as cytochrome P-448 was altered by the administration of phenobarbitone and 3-methylcholanthrene alone or in combination with 9-hydroxyellipticine. The correlation between these activities was maintained following treatment of animals with Arochlor 1254, benzo[a]pyrene, benzo[e]pyrene, 7,12-dimethylbenzo[a]anthracene,2-anthramine and 2-naphthylamine.     

UDP-glucuronosyl transferase and the conjugation of benzo(a)pyrene metabolites to DNA.

Addition of UDP-glucuronic acid to microsomal incubations containing benzo(a)pyrene caused a dose-dependent conjugation of principally quinone and phenol metabolites. Total benzo(a)pyrene oxidation was also stimulated with a maximum increase at 2 nM UDPGA. In the presence of calf thymus DNA, UDPGA caused a 2.7-fold increase in benzo(a)pyrene diol-oxide modification of DNA, as analyzed by Sephadex LH-20 chromatography. Maximum DNA modification by diol-oxides occurred at a UDPGA concentration which gave the highest level of free benzo(a)pyrene 7,8-dihydrodiol; likewise, the amount of DNA adduct derived from benzo(a)pyrene phenols declined in parallel with levels of free phenol metabolites. The UDPGA-induced increase in benzo(a)pyrene oxidation and concomitant increase in diol-oxide modification of DNA is consistent with removal of product inhibition by glucuronide conjugation of an inhibitory benzo(a)pyrene metabolite.     

A modified method for the assay of benzo(a)pyrene hydroxylase

An assay is described for the activity of benzo[a]pyrene hydroxylase. The method is based on the direct fluorimetric measurement of the metabolites of benzo[α]pyrene in alkaline medium after adding Triton X 100 to the testing sample.     

Formation and removal of benzo[a]pyrene metabolites--DNA adducts in cultured normal human fibroblasts using a microsome-activating system

The rate of removal of DNA adducts of several benzo[a]pyrene metabolites from nuclear DNA was compared by introducing a microsome-activating system in human fibroblast cells. Confluent human fibroblasts were exposed to benzo[a]pyrene in the presence of a microsomal activating system and DNA adducts were formed in the nuclear DNA. The adducts present in DNA were determined after 1 h of incubation and 48 h later. There was no difference in the rate of removal between 7S- and 7R -N2-[10-(7 beta, 8 alpha-trihydroxy-7,8,9,10- tetrahydrobenzo[a]pyrene)yl]deoxyguanosine, 7R -N2-[10(7beta, 8 alpha, 9 beta-trihydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene)yl]deoxyguanosine and the covalent adduct of 9-hydroxybenzo[a]pyrene-4,5-epoxide to guanosine. This finding does not agree with the idea that metabolites forming 'persistent DNA adducts' are always responsible for the carcinogenicity of their parent compound.     

Oxidation of benzo[a]pyrene by the filamentous fungus Cunninghamella elegans.

Cunninghamella elegans oxidized benzo[a]pyrene to several metabolic products. Compounds that were isolated and identified were: trans-9,10-dihydroxy-9,10-dihydrobenzo[a]pyrene, trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene, benzo[a]pyrene 1,6-quinone, benzo[a]pyrene 3,6-quinone, 9-hydroxybenz[a]pyrene, and 3-hydroxybenzo[a]pyrene. In addition, an unidentified dihydroxybenzo[a]pyrene metabolite was also formed. Experiments with [14C]benzo[a]pyrene showed that over a 96-h period, 18.4% of the hydrocarbon was converted to metabolic products. Most of the metabolites were sulfate conjugates as demonstrated by the formation of benzo[a]pyrene quinones and phenols after treatment with aryl sulfatase. Glucuronide and sulfate conjugates were also detected as water-soluble metabolites. The results show that benzo[a]pyrene is metabolized by a filamentous fungus in a manner that is remarkably similar to that observed in higher organisms.