Reactions of benzo]pa]pyrene diol-epoxides with DNA and nucleosomes in aqueous solutions

The rate of solvolysis of benzo[$\text{a}$]pyrene diol-epoxide in aqueous solutions can be followed by fluorescence spectroscopy. When DNA was present the rat of breakdown of benzo[$\text{a}$]pyrene diol-epoxide was substantially enhanced, while at the same time fluorescence intensity was decreased. This decrease, however, was due to noncovalently bound tetraols and does not seem to be a function of the covalent adducts formed. Nucleosomal core particles, reacted under identical conditions, showed very little quenching of the pyrene-like chromophore. When increasing amounts of cysteine were present the covalent binding could be prevented in both free DNA and nucleosomal DNA. Analysis of the distribution of the carcinogen to nucleosomal DNA showed that the covalently bound carcinogen was located at or within 10 bases of the 5′-OH region of the nucleosomal DNA.     

Lack of association between induction of dominant-lethal mutations and induction of heritable translocations with benzo[a]pyrene in postmeiotic germ cells of male mice

Benzo[a]pyrene was tested for induction of dominant-lethal mutations in germ cells of male mice. Clear-cut dominant-lethal effects were induced in middle and early spermatoza. In contrast to the dominant-lethal effects observed the study showed no detectable increase in hertiable translocations for these stages over the spontaneous level. Thus, the results provide another example of a chemical mutagen that is effective in inducing dominant-lethal mutations but relatively ineffective in inducing heritable translocations in male postmeiotic germ cells.     

Metabolite repression inhibits degradation of benzo[a]pyrene and dibenz[a,h]anthracene by Stenotrophomonas maltophilia VUN 10,003

Large inocula of Stenotrophomonas maltophilia VUN 10,003 were used to investigate bacterial degradation of benzo[a]pyrene and dibenz[a,h]anthracene. Although strain VUN 10,003 was capable of degrading 10–15 mg l⁻¹ of the five-ring compounds in the presence of pyrene after 63 days, further addition of pyrene after degradation of the five-ring polycyclic aromatic hydrocarbons (PAHs) ceased did not stimulate significant decreases in the concentration of benzo[a]pyrene or dibenz[a,h]anthracene. However, pyrene was degraded to undetectable levels 21 days after its addition. The amount of benzo[a]pyrene and dibenz[a,h]anthracene degraded by strain VUN 10,003 was not affected by the initial concentration of the compounds when tested at 25–100 mg l⁻¹, by the accumulation of by-products from pyrene catabolism or a loss of ability by the cells to catabolise benzo[a]pyrene or dibenz[a,h]anthracene. Metabolite or by-product repression was suspected to be responsible for the inhibition: By-products from the degradation of the five-ring compounds inhibited their further degradation. Journal of Industrial Microbiology & Biotechnology (2002) 28, 88–96 DOI: 10.1038/sj/jim/7000216 Received 30 January 2001/ Accepted in revised form 10 October 2001     

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.     

A new type of biological chemiluminescence: The microsomal chemiluminescence of benzo[a]pyrene arises from the diol epoxide product of the 7,8-dihydrodiol

The chemiluminescence, CL, accompanying the metabolism of the carcinogen benzo[a]pyrene, BP, by the aryl hydrocarbon hydroxylase system is a new type of low intensity biological chemiluminescence. It is the result of spontaneous oxygenation of a specific reactive metabolic intermediate; not inhibitable by superoxide dismutase or catalase. The reactive metabolite is the strongly mutagenic 7,8-dihydrodiol-9,10-epoxide, produced enzymatically from the 7,8-dihydrodiol precursor. Hydroxylation of benzo[a]pyrene at the 3 position does not lead to chemiluminescent emission; the CL quantum yields of BP and 3-OH-BP are the same. The CL quantum yields of microsomal metabolism of (?) 7,8-diol-BP and the racemic 7,8-diol-BP are identical. The kinetics of CL of the latter show a much faster initial reaction rate, correlating with the greater reactivity of diol epoxide I formed from (+) 7,8-diol-BP. CL may therefore be used to follow the pathways and the rates of production of the mutagenic diol epoxides of BP.     

污染土壤中苯并(a)芘的微生物降解途径研究进展

苯并(a)芘(BaP)是一种具有强致癌、致畸和致突变的多环芳烃(PAHs)。为了修复BaP污染的土壤,探索其降解途径是很重要的。为此,综述了国内外有关污染土壤中苯并(a)芘的微生物降解情况,对不同真菌、细菌降解苯并(a)芘的能力、代谢途径、共代谢底物以及环境影响因素进行了介绍和比较,提出了苯并(a)芘中间代谢产物的累积及其环境毒性方面的研究是修复苯并(a)芘污染土壤的重要方向。     

Structure-activity relationships of organosulfur compounds as inhibitors of cytochrome P450 1-mediated activation of benzo[a]pyrene in a human cell model

Twelve naturally-occurring organosulfur compounds were investigated as inhibitors of cytochrome P450 1 (CYP450 1)-mediated activation of benzo[a]pyrene (B[a]P) in human hepatoma (HepG2) cells. Inhibition depended on the presence of a diallyl group and the number of S atoms. Diallyl trisulfide (DATS), with a diallyl group and three S atoms, had the highest activity with an IC₅₀ of 0.4 mM, and 1.5-fold higher potency than diallyl disulfide (DADS) containing a diallyl group and two S atoms. Organosulfur compounds containing an alkyl group were less effective, or even ineffective, inhibitors of both CYP450 1 and B[a]P-induced cytotoxicity than DADS and DATS. Alliin and S-allyl cysteine containing the S-cysteinyl group had no inhibition.     

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.     

Review on proteomic analyses of benzo[a]pyrene toxicity

Benzo[a]pyrene (BaP), a five-ring polycyclic aromatic hydrocarbon, is a well-recognized environmental pollutant. Coal-processing waste products, petroleum sludge, asphalt, creosote, and tobacco smoke, all contain high levels of BaP. Exposure to BaP elicits many adverse biological effects, including tumor formation, immunosuppression, teratogenicity, and hormonal effects. In addition to the genetic damage caused by BaP exposure, several studies have indicated the disruption of protein-protein signaling pathways. However, contrary to the large number of studies on BaP-induced DNA damage, only few data have been gathered on its effects at the protein level. This review highlights all proteomic studies to date used for assessing the toxicity of BaP and its metabolites in various organ systems. It will also give an overview on the role proteomics may play to elucidate the mechanisms underlying BaP toxicity.     

Use of a cyclodextrin for increased protective activity of volatile allyl sulfides against benzo[a]pyrene-induced toxicity in human cell model

The lower inhibitory effect of allyl sulfides on benzo[a]pyrene (B[a]P)-induced toxicity in a cell culture model, rather than in an animal model, was related to their volatile natures. An improved assay system for these volatile chemicals is now suggested. When hydroxypropyl--cyclodextrin was used as an inclusion vehicle of sulfur chemicals, cell viabilities of B[a]P-treated cells were significantly increased by 30–100% and 30–80% at 100–1000 M diallyl disulfide (DADS) and 10–100 M diallyl trisulfide (DATS) treatments, respectively.     

Active transport of benzo[a]pyrene in apical membrane vesicles from normal human intestinal epithelium

Transport of the carcinogen benzo[a]pyrene in apical membrane vesicles (AMV) from normal human intestine, was investigated. Benzo[a]pyrene transport was found in AMV throughout the small intestine, but was greatest in colon. Evidence suggesting involvement of P-Glycoprotein (P-Gp), included (1) comparable transport of P-Gp substrate doxorubicin, (2) transport stimulation by ATP and (3) transport suppression by the P-Gp inhibitor, verapamil.     

苯并[a]芘暴露对三疣梭子蟹鳃、肝胰腺组织毒理学指标的影响

本文研究了三疣梭子蟹(Portunus trituberculatus)在对苯并[a]芘(BaP)富集(15 d)、释放(15d)过程中其鳃和肝胰腺组织的4种毒理学指标的响应.4种毒理学指标分别为7-乙氧基异吩噁唑酮-脱乙基酶(EROD)、谷胱甘肽硫转移酶(GST)、超氧化物歧化酶(SOD)和脂质过氧化(LPO).设置了0.05 μg/L和0.45 μg/L两个实验组以及海水和丙酮对照组.结果显示,在富集阶段,与海水对照组相比,第1天时0.05 μg/L和0.45μg/L实验组鳃、肝胰腺组织的各毒理指标均显著受到诱导(P＜0.05),诱导程度随BaP暴露浓度的增加而增大.而后鳃、肝胰腺组织的EROD、GST活性以及鳃组织的SOD活性达到峰值后下降,肝胰腺组织的SOD活性以及鳃、肝胰腺组织的丙二醛(MDA)含量则持续增加.鳃组织的EROD、GST、SOD活性到达峰值时间早于肝胰腺组织,其活性以及MDA含量也低于肝胰腺组织.在释放阶段,0.45pg/L实验组鳃组织的SOD活性,0.05μ-g/L和0.45 μg/L两个实验组肝胰腺组织的SOD活性均依然显著高于同期海水对照组水平(P＜0.05),其余各浓度实验组鳃、肝胰腺组织均能恢复到同期海水对照组水平(P＞ 0.05).实验结果表明,三疣梭子蟹的鳃组织对于BaP暴露响应时间比肝胰腺组织更早,但均具有一定的恢复能力.     

HspA1A facilitates DNA repair in human bronchial epithelial cells exposed to Benzo[a]pyrene and interacts with casein kinase 2

Benzo[a]pyrene (BaP) is a ubiquitously distributed environmental pollutant that induces deoxyribonucleic acid (DNA) damage. The inducible heat shock protein (HspA1A) can function as a molecular chaperone; however, its role in DNA repair remains largely unknown. In the present study, human bronchial epithelial cells (16HBE) stably transfected with plasmids carrying HspA1A gene or shRNAs against HspA1A were treated with BaP. DNA damage levels of the cells were evaluated by comet assay. Results suggest that HspA1A could protect cells against DNA damage and facilitate the decrease of DNA damage levels during the first 2 h of DNA repair. DNA repair capacity (DRC) of Benzo(a)pyrene diol epoxide (BPDE)-DNA adducts was evaluated by host cell reactivation assay in the stable 16HBE cells transfected with luciferase reporter vector PCMVluc pretreated with BPDE. Compared with control cells, cells overexpressing HspA1A showed higher DRC (p < 0.01 at 10 μM BPDE and p < 0.05 at 20 μM BPDE, respectively), while knockdown of HspA1A inhibited DNA repair (p < 0.05 at 10 μM BPDE). Moreover, casein kinase 2 (CK2) was shown to interact with HspA1A by mass spectrometry and co-immunoprecipitation assays. The two proteins were co-localized in the cell nucleus and perinuclear region during DNA repair, and were identified by confocal laser scanning microscope. In addition, cells overexpressing HspA1A showed an increased CK2 activity after BaP treatment compared with control cells (p < 0.01). Our results suggest that HspA1A facilitates DNA repair after BaP treatment. HspA1A also interacts with CK2 and enhances the kinase activities of CK2 during DNA repair.

Electronic supplementary material

The online version of this article (doi:10.1007/s12192-013-0454-7) contains supplementary material, which is available to authorized users.     

Chiral stationary phase high-performance liquid chromatographic resolution and absolute configuration of enantiomeric benzo[a]pyrene diol-epoxides and tetrols

Enantiomers of diastereomeric benzo[a]pyrene (BP) diol-epoxides, r-7,t-8-dihydroxy-t-9,10-epoxy-7,8,9,10-tetrahydro-BP (BP 7,8-diol-anti-9,10-epoxide), r-7,t-8-dihydroxy-c-9,10-epoxy-7,8,9,10-tetrahydro-BP (BP 7,8-diol-syn-9,10-epoxide), r-9,t-10-dihydroxy-t-7,8-epoxy-7,8,9,10-tetrahydro-BP (BP 9,10-diol-anti-7,8-epoxide), and several 7,8,9,10-tetrahydroxy-7,8,9,10-tetrahydrobenzo[a]pyrenes (BP tetrols) were resolved by high-performance liquid chromatography (HPLC) using columns packed with either (R)-N-(3,5-dinitrobenzoyl)phenylglycine[(R)-DNBPG] or (S)-N-(3,5-dinitrobenzoyl)leucine [(S)-DNBL], which is either ionically or covalently bonded to gamma-aminopropylsilanized silica. Resolution of enantiomers was confirmed by ultraviolet-visible absorption and circular dichroism spectral analyses. Resolved enantiomers of BP diol-epoxides were each hydrolyzed in acidic solution to a pair of diastereomeric tetrols which were separated by reversed-phase HPLC. Absolute stereochemistries of enantiomeric diol-epoxides were deduced by the absolute configuration of their hydrolysis products.     

Human intestinal Caco-2 cells display active transport of benzo[a]pyrene metabolites

Epithelial cells of the gastrointestinal tract are challenged by exposure to many potentially toxic agents including the well-known food contaminant benzo[a]pyrene (B[a]P). They are equipped with a variety of Phase 1- and Phase 2-enzymes that are able to metabolize B[a]P. Furthermore, transmembranous ABC-transport proteins are expressed at the apical pole of these cells. The aim of this study was to investigate whether [14C]B[a]P or products of the metabolism are transported by intestinal cells back into the gut lumen. The intestinal Caco-2 cell line was used as a metabolism and transport model. Experiments with Caco-2 monolayers in the Transwell-system revealed that radiolabeled substance is transported towards the apical (luminal) region. This transport was characterized as active and increased after induction of cytochromes P450 1A1 and 1B1 by beta-naphthoflavone. On the other hand, transport was decreased with the concomitant inhibition of Phase 1-metabolism. TLC-analysis revealed that the primary metabolites of B[a]P found in the supernatant were very polar; other metabolites of less polarity could only be detected in trace amounts. These results indicate that B[a]P is metabolized by Caco-2 cells to highly polar metabolites resulting from biphasic metabolism and that these polar metabolites are subject to an apically directed transport. Chemical inhibition studies showed that P-glycoprotein and MRP1 or 2 were not involved in this polarized B[a]P-metabolite secretion.     

Inhibition of benzo[a]pyrene-induced cytotoxicity and cytochrome P450 1A activity by dietary flavonoids in human liver cell model: structure-activity relationship

Inhibition of benzo[a]pyrene (B[a]P)-induced cytotoxicity and cytochrome p450 1A (CYP 1A) activity by flavonoids (1–100 M) was examined in terms of the structure-activity relationship in the human liver-derived cell model (HepG2). Two hydroxyl groups in the 5- and 7-position of flavonoids were essential to inhibit B[a]P-induced cytotoxicity. Generally, flavones (IC₅₀; 5.0–17.2 M) were more potent than the corresponding flavonols (IC₅₀; 42.7–131.8 M), and flavonoids such as apigenin (IC₅₀; 7.2 M) were more active than the corresponding isoflavonoids, genistein (IC₅₀; 61.7 M). The planar structure of flavone proved to be important in inhibiting B[a]P-induced toxicity and CYP 1A activity. The inhibitory effect of flavonoids on B[a]P-induced CYP 1A activity was correlated well with the inhibition of B[a]P-induced cytotoxicity (r=0.635, p<;0.01).     

Benzo[a]pyrene removal by Marasmiellus troyanus in soil microcosms

Benzo[a]pyrene (B[a]P) is a carcinogenic polyaromatic hydrocarbon that enters the environment as an incomplete combustion production of fossil fuels. Several species of filamentous fungi are capable of biotransforming and/or mineralizing B[a]P in liquid cultures, however there has been less success in soil habitats. In this study, the litter rot fungus Marasmiellus troyanus was encapsulated in alginate and delivered to B[a]P-spiked soil microcosms (100 μg B[a]P/g soil) for 1, 2 and 6 weeks, with and without a fertilizer solution. After 2 weeks, 32.5% of B[a]P was recovered from soil microcosms treated with M. troyanus compared to 55–70% for controls. After 6 weeks, controls demonstrated an average percent recovery of B[a]P of 54% while M. troyanus-inoculated samples gave an average percent recovery of 11%. Similar bioaugmentation of contaminated habitats with appropriately formulated fungi has potential for practical bioremediation in soil environments. Journal of Industrial Microbiology & Biotechnology (2000) 25, 116–119.     

四环素与3,4-苯并芘复合污染对抗性基因tetA(C)产生高抗性突变的影响

【目的】探究环境中同时存在低浓度四环素(tetracycline,TC)和3,4-苯并芘(benzo [a] pyrene,Bap)对抗性基因tetA(C)产生高抗性突变的影响。【方法】以大肠杆菌(Escherichia coli,E. coli)为宿主菌株,pACYC184质粒作为载体,四环素抗性基因tetA(C)作为研究对象,采用易错PCR构建基因文库的方法,建立基因突变位点对应高抗性的关系密码表。同时设置添加低浓度TC且添加0–30 mg/L Bap以及仅添加0–30 mg/L Bap的处理组,培养携带pACYC184质粒的大肠杆菌14 d,每组中随机挑选10株获得高抗性的菌株,对其中的tetA(C)基因片段进行测序,再结合突变位点密码表,计算高抗性菌株中由基因突变产生高抗性菌株的比例。【结果】测序结果显示在低浓度TC选择压力下,Bap浓度越高时,高抗性基因突变株占的比例也越高(P≤0.01),而不添加TC时,Bap浓度与高抗性基因突变株占比之间无变化规律(P0.05)。【结论】当环境中同时存在Bap和低浓度TC时,高抗性突变基因易于通过选择压力保存下来。