Formation of sulfate and glucoside conjugates of benzo[e]pyrene by Cunninghamella elegans

 Benzo[e]pyrene is a pentacyclic aromatic hydrocarbon, which, unlike its structural isomer benzo[a]pyrene, is not a potent carcinogen or mutagen. The metabolism of benzo[e]pyrene was studied using the filamentous fungus Cunninghamella elegans ATCC 36112. C. elegans metabolized 65% of the [9, 10, 11, 12-³H]benzo[e]pyrene and unlabeled benzo[e]pyrene added to Sabouraud dextrose broth cultures after 120 h of incubation. Three major metabolites of benzo[e]pyrene were separated by reversed-phase high-performance liquid chromatography. These metabolites were identified by ¹H and ¹³C NMR, UV-visible, and mass spectral analyses as 3-benzo[e]pyrenylsulfate, 10-hydroxy-3-benzo[e]pyrenyl sulfate, and benzo[e]pyrene 3-O-β-glucopyranoside. Received: 7 September 1995/Received revision: 14 November 1995/Accepted: 11 December 1995     

Degradation of Benzo[a]pyrene by Mycobacterium vanbaalenii PYR-1

Metabolism of the environmental pollutant benzo[a]pyrene in the bacterium Mycobacterium vanbaalenii PYR-1 was examined. This organism initially oxidized benzo[a]pyrene with dioxygenases and monooxygenases at C-4,5, C-9,10, and C-11,12. The metabolites were separated by reversed-phase high-performance liquid chromatography (HPLC) and characterized by UV-visible, mass, nuclear magnetic resonance, and circular dichroism spectral analyses. The major intermediates of benzo[a]pyrene metabolism that had accumulated in the culture media after 96 h of incubation were cis-4,5-dihydro-4,5-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-4,5-dihydrodiol), cis-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-11,12-dihydrodiol), trans-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene trans-11,12-dihydrodiol), 10-oxabenzo[def]chrysen-9-one, and hydroxymethoxy and dimethoxy derivatives of benzo[a]pyrene. The ortho-ring fission products 4-formylchrysene-5-carboxylic acid and 4,5-chrysene-dicarboxylic acid and a monocarboxylated chrysene product were formed when replacement culture experiments were conducted with benzo[a]pyrene cis-4,5-dihydrodiol. Chiral stationary-phase HPLC analysis of the dihydrodiols indicated that benzo[a]pyrene cis-4,5-dihydrodiol had 30% 4S,5R and 70% 4R,5S absolute stereochemistry. Benzo[a]pyrene cis-11,12-dihydrodiol adopted an 11S,12R conformation with 100% optical purity. The enantiomeric composition of benzo[a]pyrene trans-11,12-dihydrodiol was an equal mixture of 11S,12S and 11R,12R molecules. The results of this study, in conjunction with those of previously reported studies, extend the pathways proposed for the bacterial metabolism of benzo[a]pyrene. Our study also provides evidence of the stereo- and regioselectivity of the oxygenases that catalyze the metabolism of benzo[a]pyrene in M. vanbaalenii PYR-1.     

Model reactions of the quinone metabolites of carcinogenic hydrocarbons with t-butylthiol

Reactions of benzo[a]pyrene 1,6-dione with t-butylthiolate affords two products of conjugate addition and subsequent spontaneous reoxidation, namely, 2-t-butylthio- and 2,4-di-t-butylthiobenzo[a]pyrene 1,6-dione. Analogous reaction of benzo[a]pyrene 3,6-dione furnished only 12-t-butylthiobenzo[a]pyrene 3,6-dione. Structural assignments are based on analysis of the high-resolution 270-MHz Fourier-transform proton nmr spectra. In both products the attachment of the entering nucleophile is on an aromatic ring remote from either of the carbonyl groups, the first examples of such detected. The biological significance of these results with relation to the potential reactions of these quinones, known to be major metabolites of the carcinogen benzo[a]pyrene, with glutathione, cysteine, and proteins in vivo is discussed.     

Seasonal Biotransformation of Naphthalene, Phenanthrene, and Benzo[a]pyrene in Surficial Estuarine Sediments

Transformation rates of naphthalene, phenanthrene, and benzo[a]pyrene in oxidized surficial sediments of a polluted urban estuary, Boston Harbor, Mass., were determined over a period of 15 months. Three sites characterized by muddy sediments were selected to represent a >300-fold range of ambient polycyclic aromatic hydrocarbon (PAH) concentration. Transformation rates were determined by a trace-level radiolabel PAH assay which accounted for PAH mineralization, the formation of polar metabolites, residue, and recovered parental PAHs in sediment slurries. Transformation rates of the model PAHs increased with increasing ambient PAH concentrations. However, turnover times for a given PAH were similar at all sites. The turnover times were as follows: naphthalene, 13.2 to 20.1 days; phenanthrene, 7.9 to 19.8 days, and benzo[a]pyrene, 53.7 to 82.3 days. At specific sites, rates were significantly affected by salinity, occasionally affected by temperature, but not affected by pH over the course of the study. Seasonal patterns of mineralization were observed for each of the PAHs at all sites. The timing of seasonal maxima of PAH mineralization varied from site to site. Seasonal potential heterotrophic activities as measured by acetate and glutamate mineralization rates did not always coincide with PAH mineralization maxima and minima, suggesting that the two processes are uncoupled in estuarine sediments.     

New procedure of high-voltage electrophoresis in polyacrylamide gel and its application to the sequencing of nucleic acids.

Addition of primary organic amines, such as n-butylamine, to the mobile phase altered the capacity factors and selectivity of benzo[a]pyrene metabolites obtained with reverse-phase high pressure liquid chromatography on an ODS column. Separation of benzo[a]pyrene phenols in particular was improved with 8 of the 10 available metabolites resolved, including those known to be biologically produced. The method offers sufficiently improved resolution or convenience that it should prove useful in comparative studies of metabolism of benzo[a]-pyrene and other polynuclear aromatic hydrocarbons. Applying the method to analysis of benzo[a]pyrene metabolites produced in vitro by hepatic microsomes from the marine fish Stenotomus versicolor indicated the principal phenolic derivatives produced by this fish were 1-hydroxy-, 3-hydroxy-, 7-hydroxy-, and 9-hydroxybenzo[a]pyrene.     

Degradation of eight highly condensed polycyclic aromatic hydrocarbons by Pleurotus sp. Florida in solid wheat straw substrate

The degradation of eight unlabeled highly condensed polycyclic aromatic hydrocarbons (PAH) and the mineralization of three ¹⁴C-labeled PAH by the white-rot fungus Pleurotus sp. Florida was investigated. Three concentrations containing 50, 250 or 1250 μg each unlabeled PAH/5 g straw were added to sterile sea sand. Selected treatments were added subsequently with ¹⁴C-labeled pyrene, benzo[a]anthracene or benzo[a]pyrene. The PAH-loaded sea sand was then mixed into straw substrate and incubated. The disappearance of the unlabeled four-to six-ring PAH: pyrene, benzo[a]anthracene, chrysene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, dibenz[a,h]anthracene and benzo[ghi]perylene, was determined by high-performance liquid chromatography. After 15 weeks of incubation, the recoveries were less than 25% for initial amounts of 50 μg (controls above 85%). The recoveries of unlabeled PAH increased in the inoculated samples with increasing concentrations applied. No correlation could be determined between the number of condensed rings of the PAH and the recoveries of added PAH. Pleurotus sp. Florida mineralized 53% [¹⁴C]pyrene, 25% [¹⁴C]benzo[a]anthracene and 39% [¹⁴C]benzo[a]pyrene to ¹⁴CO₂ in the presence of eight unlabeled PAH (50 μg applied) within 15 weeks. During the course of cultivation, Pleurotus sp. Florida degraded more than 40% of the wheat straw substrate. Variation of the initial concentration of PAH did not influence the extent of degradation of the organic matter. Received: 16 December 1996 / Received revision: 17 March 1997 / Accepted: 22 March 1997     

4S polycyclic aromatic hydrocarbon receptor (glycine N‐methyltransferase) and the aryl hydrocarbon receptor nuclear translocator (hypoxia inducible factor‐1β) interaction in Chinese hamster ovary and rat hepatoma cells: 4S PAH‐R/ARNT hetero‐oligomers?

Rat CYP1A1 promoter‐luciferase, transiently transfected wild‐type and 4S PAH receptor (glycine N‐methyl transferase, GNMT)‐transformed Chinese hamster ovary (CHO) cells were exposed to benzo[a]pyrene and assayed for luciferase activity as an indicator of CYP1A1 promoter activity. CHO cells transformed with the rat 4S PAH receptor/GNMT expression vector had twice the induction level of luciferase activity with respect to wild‐type CHO cells in concert with previously published reports that the 4S PAH receptor/GNMT mediates benzo[a]pyrene induction of CYP1A1 gene expression. Lysates of GNMT‐transformed CHO cells and wild‐type H4IIE rat hepatoma cells exposed to benzo[a]pyrene were immuno‐precipitated with anti‐GNMT antibodies, separated by SDS–polyacrylamide gel electrophoresis and transferred to PVDF membrane for Western blot analysis with anti‐aryl hydrocarbon receptor nuclear translocator (ARNT, HIF‐1β) antibodies. Results of this analysis indicated that the 4S PAH receptor/GNMT forms a hetero‐oligomer (dimer?) with ARNT/HIF‐1β which dissociates in the presence of B[a]P. These observations further indicate the role of GNMT (which has been shown to be multifunctional) and B[a]P in the induction of CYP1A1 and also a potential role of GNMT in the modulation of hypoxia inducible factor‐1 function with respect to the HIF‐1β subunit (ARNT). J. Cell. Biochem. 112: 2015–2018, 2011. © 2011 Wiley‐Liss, Inc.     

Oxidation of polycyclic aromatic hydrocarbons by the bacterial laccase CueO from E. coli

Laccases produced by white rot fungi are capable of rapidly oxidizing benzo[a]pyrene. We hypothesize that the polycyclic aromatic hydrocarbon (PAH)-degrading bacteria producing laccase can enhance the degree of benzo[a]pyrene mineralization. However, fungal laccases are glycoproteins which cannot be glycosylated in bacteria, and there is no evidence to show that bacterial laccases can oxidize benzo[a]pyrene. In this study, the in vitro oxidation of PAHs by crude preparations of the bacterial laccase, CueO, from Escherichia coli was investigated. The results revealed that the crude CueO catalyzed the oxidation of anthracene and benzo[a]pyrene in the same way as the fungal laccase from Trametes versicolor, but showed specific characteristics such as thermostability and copper dependence. In the presence of 2,2'-azino-bis-(3-ethylbenzothiazoline-6-sulfonic acid), high amounts of anthracene and benzo[a]pyrene, 80% and 97%, respectively, were transformed under optimal conditions of 60°C, pH 5, and 5 mmol l(-1) CuCl(2) after a 24-h incubation period. Other PAHs including fluorene, acenaphthylene, phenanthrene, and benzo[a]anthracene were also oxidized by the crude CueO. These findings indicated the potential application of prokaryotic laccases in enhancing the mineralization of benzo[a]pyrene by PAH-degrading bacteria.     

Metabolism of benzo[a]pyrene: Effect of 3-methylcholanthrene pretreatment on metabolism by microsomes from lungs of genetically “responsive” and ”nonresponsive” mice

The metabolism of [¹⁴C]benzo[a]pyrene by microsomes from the lungs of normal and 3-methylcholanthrene-treated DBA/2J, C57BL/6J, and A/HeJ mouse strains was quantitatively analyzed by high-pressure liquid chromatography. The ratio of dihydrodiols of benzo[a]pyrene to total metabolites formed was greater with lung microsomes than with liver microsomes in all three strains. The ratio of epoxide hydrase to monooxygenase activity in mouse lung was shown to be considerably higher than in mouse liver. Benzo[a]pyrene metabolism by control lung microsomes showed some strain differences. C57BL/6J and A/HeJ mice formed twice as much dihydrodiols as a percentage of total metabolism compared to DBA/2J mice. DBA/2J mice produced somewhat less phenol 2 fraction and considerably more quinone 1 and 2 fractions than the other two mouse strains as a percentage of total metabolism. Treatment of C57BL/6J and DBA/2J mice with 3-methylcholanthrene resulted in a 20-fold increase in the metabolism of benzo[a]pyrene, while A/HeJ mice were induced more than 50-fold. The profiles of metabolites from the 3-methylcholanthrene-induced animals were nearly identical in all three mouse strains.     

The metabolism of benzo[a]pyrene phenols by rat liver microsomal fractions

The oxidative metabolism of benzo[a]pryrene (B[a]P) phenols catalyzed by liver microsomes in vitro leads to multiple products. High-pressure liquid chromatography analysis of the organic-soluble products formed indicates that regardless of the animal pretreatment regime, 3-hydroxy-B[a]P is metabolized to the 3,6-quinone and to a hydroxylated derivative tentatively identified as 3,9-dihyroxy-B[a]P. However, the distribution of products obtained with 9-hydroxy-B[a]P varied with animal pretreatment. A maximum of three distinct metabolites was obtained when the 9-phenol was metabolized in vitro with microsomes from phenobarbital-pretreated rats and the tentative 3,9-dihydroxy derivative was a common metabolite for all pretreatment regimes. Physical characterization, including mass spectrometry, indicates that all three products have an extra oxygen atom incorporated into their molecular structure from molecular oxygen. Studies utilizing specific inhibitors of the cytochrome P-450-dependent monooxygenase clearly suggest that the formation of dihydroxy or phenol-oxide derivatives is catalyzed by the hemoprotein, cytochrome P-450. These metabolites of the benzo[a]pyrene phenols are most likely related to the putative phenol-oxides of benzo[a]pyrene which have been demonstrated to alkylate DNA and protein. Repetitive scan difference spectrophotometric analysis of incubation mixtures containing rat liver microsomes, 3- or 9-hydroxy-B[a]P, NADPH, and oxygen shows the conversion of the phenols into products which absorb in the region from 400 to 500 nm. During and after the steady state of the reaction, it can be seen that certain of the hydroxy compounds produced are in equilibrium with their respective quinone form and may be involved in an oxygen-coupled redox cycle.     

Predicting the Efficacy of Polycyclic Aromatic Hydrocarbon Bioremediation in Creosote-Contaminated Soil Using Bioavailability Assays

Nonexhaustive extraction (propanol, butanol, hydroxypropyl-β-cyclodextrin [HPCD]), persulfate oxidation and biodegradability assays were employed to determine the bioavailability of polycyclic aromatic hydrocarbons (PAHs) in creosote-contaminated soil. After 16 weeks incubation, greater than 89% of three-ring compounds (acenaphthene, anthracene, fluorene, and phenanthrene) and 21% to 79% of four-ring compounds (benz[a]anthracene, chrysene, fluoranthene, and pyrene) were degraded by the indigenous microorganisms under biopile conditions. No significant decrease in five- (benzo[a]pyrene, benzo[b+k]fluoranthene) and six-ring compounds (benz[g,h,i]perylene, indeno[1,2,3-c,d]pyrene) was observed. Desorption of PAHs using propanol or butanol could not predict PAH biodegradability: low-molecular-weight PAH biodegradability was underestimated whereas high-molecular-weight PAH biodegradability was overestimated. Persulfate oxidation and HPCD extraction of creosote-contaminated soil was able to predict three- and four-ring PAH biodegradability; however, the biodegradability of five-ring PAHs was overestimated. These results demonstrate that persulfate oxidation and HPCD extraction are good predictors of PAH biodegradability for compounds with octanol-water partitioning coefficients of < 6.     

The DNA binding of benzo[alpha]pyrene metabolites catalysed by rat lung microsomes in vitro and in isolated perfused rat lung.

When [³H]benzo[a]pyrene is incubated in vitro together with DNA, NADPH and rat lung microsomes, covalent binding of benzo[a]pyrene (BP) metabolites to DNA occurs. These metabolite-nucleoside complexes can be resolved into several distinct peaks by elution of a Sephadex LH-20 column with a water-methanol gradient. 3-Methylcholanthrene (MC) pretreatment of animals induces the total covalent binding in vitro several-fold and increases the amounts of at least five metabolite-nucleoside complexes associated with the 7,8-diol-9,10-epoxidcs, the 7,8-oxide or quinones oxygenated further, the 4,5-oxide and phenols oxygenated further. These increases correspond well with the increases in the production of both non-K-region and K-region metabolites of BP by lung microsomes, as determined by highpressure liquid chromatography (HPLC). On the other hand, when [³H]BP is metabolized in isolated perfused rat lung, only the peak representing the 7,8-diol-9,10-epoxide bound to nucleoside(s) is readily detectable and then only in lungs from MC-treated animals. The extent of binding of BP metabolites to lung DNA is very low, about 0.0004% of the total dose applied to the perfusion medium; more than 60% of this can be accounted for by the binding of the 7,8-diol-9,10-epoxides to nucleoside(s). It is suggested that the further metabolism leading to metabolites not available to covalent binding, (e.g. conjugation) of primary BP metabolites in the intact tissue is responsible for the differences in the metabolite-nucleoside patterns observed in vivo, as compared with microsomal metabolism in vitro.     

Covalent binding of benzo[a]pyrene to cytochrome P-450βNF-B2 and other proteins in reconstituted mixed-function oxidase systems

A reconstituted mixed-function oxidase system, containing the major β-naphthoflavone-induced isozyme of rat liver cytochrome P-450 bound benzo[a]pyrene covalently in the presence of NADPH. NADPH-cytochrome P-450 reductase was required for binding and a maximum rate of adduct formation was obtained at 8 units of reductase per nmol cytochrome P-450. Phosphatidylcholine inhibited this reaction. Benzo[a]pyrene was bound to the cytochrome, but not to the reductase, as shown by sodium dodecyl sulfate (SDS)-polyacrylamide gel electrophoresis. Approximately 6 molecules of benzo[a]pyrene bound to each molecule cytochrome P-450 during prolonged incubations. No binding occurred when the β-naphthoflavone-induced isozyme of cytochrome P-450 was replaced by the major isozyme induced by phenobarbital, but both cytochromes incorporated benzo[a]pyrene to approximately the same extent when they were incubated together in the presence of the reductase and NADPH. Metabolically activated benzo[a]pyrene also bound covalently to purified epoxide hydrodrolase, when this enzyme was added to the reconstituted mixed-function oxidase system.     

Non-enzymic activation of polycyclic aromatic hydrocarbons as mutagens.

Samples of 22 polycyclic aromatic hydrocarbons and related derivatives were subjected to ⁶⁰Co gamma radiation in air, and the irradiated samples were tested for mutagenicity with the Salmonella typhimurium strains TA 98, TA 1535, TA 1537, and TA 1538. Testing was conducted with the bacterial strains alone, thus not fortified with liver-microsomal enzymes or other metabolizing systems. Marked mutagen responses were obtained for several irradiated samples with the TA 98, TA 1537, and TA 1538 strains but not with the TA 1535 strain. Irradiated samples of benzo[a]anthracene, benzanthrone, benozo[g,h,i]perylene, benzo[a]pyrene, chrysene, fluorene, 9-methylanthracene, 1-methylphenanthrene, 2-methylphenanthrene, and pyrene gave positive mutagenic tests and dose-responses, whereas unirradiated control samples of these were inactive. Acenaphthene, phenanthrene, and phenanthrenequinone exhibited toxicity which interfered with interpretation of mutagenicity testing. Samples of 2-methylanthracene and tetracene were mutagenic with or without irradiation. Alizarin, anthracene, anthraquinone, anthrone, dobenzo[a,h]anthracene, picene, and triphenylene negative results. Samples of benzo[a]pyrene adsorbed on silica gel irradiated in air by ⁶⁰Co gamma radiation or by 254 nm ultraviolet light and samples adsorbed on filter paper irradiated by visible light yielded preparations mutagenic towards the TA 98, TA 1537, and TA 1538 strains. These results suggest that parent polycyclic aromatic hydrocarbons not themselves mutagenic towards S. typhimurium may be oxidized in air by radiation-induced processes to products whose mutagenicity resembles that of liver-microsomal metabolites of the parent polycyclic aromatic hydrocarbon.     

糙皮侧耳和鞘脂菌NS7对多环芳烃污染土壤的生物强化与协同作用

【背景】真菌和细菌被认为在多环芳烃污染土壤生物修复过程中发挥协同作用,目前在真实土壤体系中开展真菌-细菌协同降解研究较少。【目的】研究真菌和细菌对不同种类多环芳烃降解的差异及对蒽和苯并[a]蒽的生物强化与协同作用。【方法】选用多环芳烃降解真菌和细菌各一株,在液体纯培养体系下分析它们对不同种类多环芳烃降解的差异,在土壤体系中采用放射性同位素示踪技术研究2种微生物对蒽和苯并[a]蒽的生物强化与协同作用。【结果】供试细菌鞘脂菌NS7能够很好地降解低环种类多环芳烃,以蒽作为唯一碳源时可以将其完全降解,在复合污染条件下对菲、蒽、荧蒽、芘等降解效果突出(>90%),对苯并[a]芘降解效果较差(9.76%)。相比而言,供试真菌糙皮侧耳菌对苯并[a]芘具有更好的降解效果(21.18%),对低环多环芳烃降解效果明显不如降解菌NS7。在自然土壤中,蒽和苯并[a]蒽具有明显不同的矿化效率,分别为18.61%和4.28%,在蒽污染土壤中加入鞘脂菌NS7并未显著提高蒽的矿化率(P>0.05),相比而言,苯并[a]蒽污染土壤中加入糙皮侧耳显著提高了污染物矿化效率(2.24倍),表明真菌和细菌在土壤环境...     

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.     

Biodegradation and sorption of polyaromatic hydrocarbons by Phanerochaete chrysosporium

The ability of the white-rot fungus Phanerochaete chrysosporium (INA-12) to degrade various polynuclear aromatic hydrocarbons (PAH) was investigated. Under static, non-nitrogen-limiting conditions, P. chrysosporium mineralized both phenanthrene and benzo[a]pyrene. Total mineralization, based on radioactive tracing, was limited to 1.8%–3% for phenanthrene and benzo[a]pyrene respectively. In both cases the pattern of mineralization did not correlate temporally with the production of lignin peroxidase activity. Sorption of radiolabelled material to the biomass was very significant with 22% and 40% of the total radioactivity being sorbed for benzo[a]pyrene and phenanthrene respectively. A number of models were examined to predict the sorption isotherms, the best performance being obtained with a three-parameter empirical model. It is apparent that lignin peroxidase is not necessarily involved in the biodegradation of all PAH and that a significant factor in PAH biodegradation and/or disappearance in cultures with the intact fungus may be attributed to sorption phenomena.     

Differential repair of polycyclic aromatic hydrocarbon DNA adducts from an actively transcribed gene

Polycyclic aromatic hydrocarbons (PAHs) are carcinogens with varying potencies. These compounds are metabolized to diol epoxides that react to form DNA adducts. Nucleotide excision repair is a critical cellular defense against these bulky DNA adducts which, if not repaired, can lead to mutations and the initiation of cancer. The structural features of the PAH-adducts play a role in differential repair of these adducts by the global genomic repair subpathway of nucleotide excision repair. DNA adducts derived from the PAHs containing bay-regions are repaired more rapidly than adducts derived from PAHs containing fjord-regions. We have employed the host cell reactivation assay to examine the rate of repair of these adducts in an actively transcribing gene. The pGL3 plasmid containing a luciferase gene was damaged with diol epoxides of benzo[a]pyrene (B[a]P-DE), dibenzo[a,l]pyrene (DB[a,l]P-DE), benzo[g]chrysene (B[g]Ch-DE), and benzo[c]phenanthrene (B[c]Ph-DE). The plasmids were transfected into B-lymphocytes with normal repair capacity as well as lymphocytes derived from patients with the XP-A, XP-C and CS-B syndromes. We found that XPA cells were able to transcribe slowly past B[g]Ch-adducts but not the other PAHs. Using the amount of luciferase produced as a measure of DNA repair, we found that the relative rates of repair in the actively transcribing luciferase gene was B[a]P-DE > DB[a,l]P-DE, B[g]Ch-DE, >B[c]Ph-DE in repair proficient and XP-C cells. These results indicate that the abilities to transcribe past and to repair the PAH adducts are dependent on different structural features of the DNA adducts.     

Removal and transformation of high molecular weight polycyclic aromatic hydrocarbons in water by live and dead microalgae

The removal and transformation of seven high molecular weight polycyclic aromatic hydrocarbons (PAHs), namely benz[a]anthracene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, dibenzo[a,h]anthracene, indeno[1,2,3-c,d]pyrene and benzo[g,h,i]perylene, by a freshwater microalga Selenastrum capricornutum under gold and white light irradiation was studied. The two light sources did not result in significant differences in the biodegradation of the selected PAHs in live algal cells, but white light was more effective in promoting photodegradation than was gold light in dead cells. The removal efficiency of seven PAHs, as well as the difference between live and dead microalgal cells, was PAH compound-dependent. Benz[a]anthracene and benzo[a]pyrene were highly transformed in live and dead algal cells, and dead cells displayed greater transformation levels than live cells. Further investigation comparing the transformation of single PAH compound, benzo[a]pyrene, by S. capricornutum and another green microalgal species, Chlorella sp., demonstrated that the transformation in dead cells was similar, indicating the process was algal-species independent. Dead algal cells most likely acted as a photosensitizer and accelerated the photodegradation of PAHs.     

Rat liver homogenate (S9)-mediated binding of benzo[a]pyren to DNA in V79 cells,V79 cell nuclei and aqueous solution

The role of the target cell in determining the structures and the amounts of hydrocarbon-DNA adducts formed after hydrocarbon activation by an exogenous metabolic ativation system was investigated by exposing intact cells of the Chinese hamster lung cell line V79, V79 cell nuclei and calf thymus DNA to benzo[a]pyrene (B[a]P) in the presenceof a rat liver homogenate activation system (S9). The DNA was isolated, enzymatically degraded to deoxyribonucleosides and the B[a]P-deoxyribonucleoside adducts analyzed by high-performance liquid chromatography. Two major adducts were present in all samples; one formed by reaction of r-7, t-8-dihydroxy-t-9, 10-epoxy-7, 8, 9, 10-tetrahydro-B[a]P (anti-B[a]PDE) with the 2-amino group of deoxyguanosine, the other formed by reaction of a metabolite of 9-hydroxybenzo[a]pyrene (9-OH-B[a]P) with an unidentified deoxyribonucleoside. The ratios of the anti-B[a]PDE-DNA adduct to the 9-OH-B[a]P-DNA adduct were: calf thymus DNA, 3 to 1: DNA from V79 nuclei, 8 to 1; DNA from intact V79 cells, 11 to 1. Similar several-fold increases in the proportion of anti-B[a]PDE-DNA adducts in V79 cells over those in calf thymus DNA were observed for a dose range of 1–10 μg B[a]P per ml. The relative extent of binding of the activated metabolite of 9-OH-B[a]P to DNA was also much lower in intact V79 cells than in calf thymus DNA after exposure to 9-OH-B[a]P in the presence of the S9 activation system.These results demonstrate that the relative abilities of various reactive bbenzo[a]pyrene metabolites formed by an exogenous activation system to reach DNA differ substantially. Therefore, assessment of the biological activity of hydrocarbons in mutation assays using exogenous activation systems must take into account not only the amounts of different reactive hydrocarbon metabolites formed but also the relative abilities of these metabolites to reach the DNA of the target cell.