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Sulfotransferase-mediated activation of 4-hydroxy- and 3,4-dihydroxy-3,4-dihydrocyclopenta[c,d]pyrene, major metabolites of cyclopenta[c,d]pyrene.

Cyclopenta[c,d]pyrene, a ubiquitous environmental and occupational pollutant, has been reported to be metabolically activated through epoxidation at the 3,4 double bond in the cyclopenta ring to produce an electrophilic and mutagenic cyclopenta[c,d]pyrene-3,4-epoxide. 4-Hydroxy-3,4-dihydrocyclopenta[c,d]-pyrene (4-HDCPP) and 3,4-dihydroxy-3,4-dihydrocyclopenta[c,d]pyrene (3,4-DHDCPP) are known to be major metabolites of cyclopenta[c,d]pyrene, which appear to be derived from cyclopenta[c,d]pyrene-3,4-epoxide. The present study was undertaken to determine whether 4-HDCPP or 3,4-DHDCPP can be further activated via the formation of reactive benzylic sulfuric acid ester metabolites. Thus, when 4-HDCPP or 3,4-DHDCPP was incubated with calf thymus DNA in the presence of rodent liver cytosol and the sulfo group donor, 3'-phosphoadenosine-5'-phosphosulfate, a significant covalent DNA binding was observed. This cytosol- and 3'-phosphadenosine-5'-phosphosulfate-dependent DNA binding was inhibited by 2,6-dichloro-4-nitrophenol and dehydroepiandrosterone, suggesting the involvement of both phenol and hydroxysteroid sulfotransferases in the activation of 4-HDCPP and 3,4-DHDCPP. A gender difference was observed for the hepatic cytosolic sulfotransferase activity for 4-HDCPP in rats (i.e., male > female). Of the two isomers of 3,4-DHDCPP, the trans-diol produced DNA adducts to a much greater extent than did the cis counterpart by sulfotransferase. 4-HDCPP and 3,4-DHDCPP were also mutagenic toward bacteria in the presence of hepatic cytosol and 3'-phosphadenosine-5'-phosphosulfate. The chemically synthesized sulfuric acid ester 4-sulfooxy-3,4-DCPP was directly mutagenic without any activation system. The data from this study suggest that sulfotransferase plays an important role in the activation of those secondary benzylic hydroxyl metabolites derived from cyclopenta[c,d]pyrene-3,4-epoxide and, possibly, from epoxides of other aromatic hydrocarbons.

Animals↗

Metabolism of benzo[a]pyrene: conversion of (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene to highly mutagenic 7,8-diol-9,10-epoxides.

Metabolites of (+/-)-trans 7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene formed by a rat liver microsomes and by a highly purified monoxygenase system were analyzed by high-pressure liquid chromatography. Four stereoisomeric tetraols of 7,8,9,10-tetrahydrobenzo[a]pyrene, known solvolysis products of the two highly mutagenic stereoisomers of the 9,10-epoxide of the 7,8-dihydrodiol, were identified as products. The ratio of the two highly unstable diol epoxides formed (7 beta,8alpha-dihydroxy-9beta,10beta-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene, diol epoxide 1; 7beta,8alpha-dihydroxy-9alpha,10alpha-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene, diol epoxide 2) ranged from about 1.7 to 0.4. The diol epoxides are sufficiently reactive to alkylate phosphate buffer (pH 7.4) at 37 degrees. Microsomes, particularly those from control animals, formed a substantial amount of an additional metabolite that appears to be phenolic. In analogy to benzo[a]pyrene, the metabolism of the 7,8-dihydrodiol shows similar induction after pretreatment of rats with phenobarbital or 3-methylcholanthrene. Neither diol epoxide appears to be a substrate for epoxide hydrase based on the ratis of tetraols formed in the presence or absence of epoxide hydrase. In view of the known carcinogenicity of benzo[a]pyrene 7,8-oxide and 7,8-dihydrodiol and of the marked mutagenicity of the stereoisomeric diol epoxides, both of these diol epoxides qualify for consideration as "ultimate carcinogen(s)" of benzo[a]pyrene.

Animals↗

(+/-)-7alpha,8beta-dihydroxy-9beta,10beta-epoxy-7,8,9,10-tetrahydrobenzo(a)-pyrene is an intermediate in the metabolism and binding to DNA of benzo(a)pyrene.

The addition of borate buffer to the aqueous methanol used to elute hydrocarbon-deoxyribonucleoside derivatives from an LH 20 Sephadex column resulted in the separation of the products of reaction with DNA of the stereoisomers, (+/-)7alpha,8beta-dihydroxy-9alpha,10alpha-epoxy- and (+/-)-7alpha,8beta-dihydroxy-9beta,10beta-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrenes, i.e., the syn- and anti-benzo(a)pyrene-diolepoxide, respecitvely. By this technique it was shown that the microsome-mediated binding to DNA of benzo(a)pyrene-7,8-dihydrodiol involved exclusively the anti-benzo(a)pyrene-diolepoxide. The benzo(a)pyrene binding to DNA that resulted on exposure of BHK21/C13 cells to this carcinogen was also shown to result predominantly by reaction of the anti-benzo(a)pyrene-diolepoxide. However, in this case other derivatives, including the syn-benzo(a)pyrene diolepoxide, might also be involved.

Animals↗

Nonenzymatic reduction of benzo(a)pyrene diol-epoxides to trihydroxypentahydrobenzo(a)pyrenes by reduced nicotinamide adenine dinucleotide phosphate.

The diol-epoxide r-7,t-8-dihydroxy-t-9,10-oxy-7,8,9,10-tetrahydrobenzo(a)pyrene is a potent mutagen and possibly the ultimate carcinogenic form of benzo(a)pyrene. A (7/8,9)-trihydroxy-7,8,9,10,10-pentahydrobenzo(a)pyrene is formed from the diol-epoxide r-7,t-8-dihydroxy-t-9,10-oxy-7,8,9,10-tetrahydroxybenzo(a)pyrene by reduction with reduced nicotinamide adenine dinucleotide phosphate. Its formation is linear with reduced nicotinamide adenine dinucleotide phosphate concentration and does not require the presence of enzyme. A (7,9/8)-trihydroxy-7,8,9,10,10-pentahydrobenzo(a)pyrene is similarly formed from the diol-epoxide r-7,t-8-dihydroxy-c-9,10-oxy-7,8,9,10-tetrahydrobenzo(a)pyrene by reduction with reduced nicotinamide adenine dinucleotide phosphate. The structures of the trihydroxypentahydrobenzo(a)pyrenes were established by their ultraviolet absorption and mass spectra and their reaction with potassium triacetylosmate.

Benzopyrenes↗

Pyrene and benzo(a)pyrene metabolism by an Aspergillus terreus strain isolated from a polycylic aromatic hydrocarbons polluted soil.

A strain of Aspergillus terreus was isolated from a polycyclic aromatic hydrocarbons (PAHs) polluted soil. The metabolism of pyrene and benzo(a)pyrene by this fungus was investigated in liquid submerged culture added of 50 and 25 ppm respectively of each compound. Depletion of pyrene and Benzo(a)pyrene was evident during the first stages of growth and was 60% and 27.5% respectively of the added amount after nine days of culture. Solvent extracts of the fermentation broth and mycelium were analysed for presence of metabolites by HPLC-MS technique. Under the present cultural conditions pyrene was mainly metabolised to pyrenylsulfate similarly to benzo(a)pyrene that led to benzo(a)pyrenylsulfate. The structure of 1-pyrenilsulfate was determined after purification of extracts and H-NMR analysis. The result show that the isolated A. terreus strain metabolises PAHs by reaction similar to those previously reported for non lignolinolytic fungi with a mechanism that suggests the hydroxylation by a cytochrome P-450 monooxygenase followed by conjugation with sulfate ion.

Aspergillus↗

Carcinogenic and non-carcinogenic aromatic hydrocarbons in lipid membranes. A fluorescence study of pyrene and benzo[a]pyrene.

1. The fluorescence behavior of a non-carcinogenic (pyrene) and a carcinogenic (benzo[a]pyrene) aromatic hydrocarbon was examined in the presence of a phospholipid bilayer membrane in the gel phase. 2. The monomer emission spectrum of pyrene in the membrane is very similar to that in micelles indicating a site near the aqueous surface region. Benzo[a[pyrene monomer spectra exhibit a red shift in the membrane relative to aliphatic hydrocarbon solvents. On the basis of spectral shifts in other homogeneous solvents, it is inferred that the carcinogen is located in the upper portion of the membrane acyl region, a more polarizable environment than the hydrocarbon core of the bilayer. 3. Analysis of the excimer to monomer emission intensity ratio as a function of probe molar ratio indicates that pyrene is much less soluble in the membrane than benzo[a]pyrene. 4. These results complement published EPR data which show that carcinogenic aromatic hydrocarbons cause structural changes in the membrane, while non-carcinogenic ones do not. These differences in membrane solubility and ability to alter membrane structure are discussed in the context of the different carcinogenic potencies of the hydrocarbons.

1,2-Dipalmitoylphosphatidylcholine↗

In vivo formation of benzo(alpha)pyrene diol epoxide-deoxyadenosine adducts in the skin of mice susceptible to benzo(alpha)pyrene-induced carcinogenesis.

The hydrocarbon-deoxyribonucleoside adducts formed in mouse skin DNA have been determined following topical application of an initiating dose of benzo(a)pyrene to Swiss mice, a strain shown to be susceptible to benzo(a)pyrene-induced skin carcinogenesis. Several DNA-bound products were formed, of which the major one (60% of total adducts), in agreement with other workers' findings, was derived from reaction of (+/-) 7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10-tetrahydrobenzo(alpha)pyrene (BDE) with the exocyclic aminogroup of deoxyguanosine. A further product (9-10% of total adducts), previously observed only after microsomal activation of benzo(a)pyrene, was observed and co-chromatographed with a further metabolite of 9-hydroxybenzo(alpha)pyrene bound to an uncharacterized base in the DNA. Two otherr products (2-3% of total adducts) were also found in the in vivo studies which co-chromatographed with BPDE-deoxyadenosine adducts and arose from cis and trans addition of the exocyclic amino group of deoxyadenosine to the 7R form, but not the 7S form, of BPDE. In contrast to this, the major in vitro deoxyadenosine-bound products, formed following reaction of BPDE with calf-thymus DNA, were derived from the 7S form of BPDE, suggesting either stereoselective formation or reaction of the 7R form of BPDE in mouse skin in vivo. Similar amounts of BPDE-deoxyguanosine and BPDE-deoxyadenosine adducts, as well as those derived from further metabolism of 9-hydroxybenzo(alpha)pyrene were formed in three strains of mice reported to have widely differing susceptibilities to polycyclic hydrocarbon-induced skin carcinogenesis. The relevance of these different hydrocarbon-DNA adducts to carcinogenesis requires further investigation.

Animals↗

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 benzo[a]pyrene and benzo[a]pyrene, 7,8-dihydrodiol and binding of benzo[a]pyrene 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 micrograms/ml) enhanced the toxicity of benzo[a]pyrene 7,8-dihydrodiol in human bronchial epithelial cells. In contrast, ellagic acid at concentrations of 1.5 and 3.0 micrograms/ml inhibited binding of benzo[a]pyrene metabolites 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.

Benzo(a)pyrene↗

Effects of acetylenic and olefinic pyrenes upon cytochrome P-450 dependent benzo[a]pyrene hydroxylase activity in liver microsomes.

1-Ethynylpyrene, trans-, & cis-1-(2-bromovinyl)pyrene, methyl 1-pyrenyl acetylene, and phenyl 1-pyrenyl acetylene are substrates for cytochrome P-450 dependent monooxygenases and also inhibitors of cytochrome P-450 dependent benzo[a]pyrene hydroxylase activities in liver microsomes from 5,6-benzoflavone or phenobarbital pretreated rats. 1-Ethynylpyrene, trans-1-(2-bromovinyl)pyrene, and methyl 1-pyrenyl acetylene cause a mechanism based inhibition (suicide inhibition) of the benzo[a]pyrene hydroxylase activities in microsomes from 5,6-benzoflavone or phenobarbital pretreated rats, while cis-1-(2-bromovinyl)pyrene only causes suicide inhibition of the hydroxylse activities in the 5,6-benzoflavone induced microsomes and phenyl 1-pyrenyl acetylene does not cause a detectable suicide inhibition of these activities in either type of microsome. Incubation with NADPH and 1-ethynylpyrene, trans-, or cis-1-(2-bromovinyl)pyrene causes a loss of the P-450 content in the microsomes from 5,6-benzoflavone or phenobarbital pretreated rats, but incubations with methyl 1-pyrenyl acetylene or phenyl 1-pyrenyl acetylene did not cause a loss of the P-450 content of either microsomal preparation.

Animals↗

Pyrrolizidine alkaloid-induced alterations in benzo[alpha]pyrene metabolism and binding of benzo[alpha]pyrene metabolites to deoxyribonucleic acid.

Pretreatment of rats by oral administration of jacobine, a pyrrolizidine alkaloid and inducer of epoxide hydrolase, produced a marked shift in hepatic microsomal metabolism in vitro of benzo[alpha]pyrene. The formation of 9-hydroxybenzo[alpha]pyrene and 7,8-dihydroxy-7,8-dihydrobenzo[alpha]pyrene was decreased whereas the formation of 4,5-dihydroxy-4,5-dihydrobenzo[alpha]pyrene was increased following jacobine treatment. This shift in the ratio of benzo[alpha]pyrene metabolites was accompanied by a significant reduction in DNA binding. Addition of purified epoxide hydrolase to control or jacobine microsomes produced a similar decrease in total DNA binding. Chromatography of benzo[alpha]pyrene metabolite-DNA nucleoside adducts showed a marked reduction in four peaks and the elimination of one peak with microsomes from jacobine-treated rats.

Animals↗

Urinary excretion of 3-hydroxy-benzo[a]pyrene after percutaneous penetration and oral absorption of benzo[a]pyrene in rats.

A method for the monitoring of exposure to benzo[a]pyrene was applied to rat urine samples. Benzo[a]pyrene was administered percutaneously and orally with repeated doses of 10, 20 and 50 mumol/kg body wt. At low dose levels, the urinary excretion of 3-OH-benzo[a]pyrene was higher after percutaneous treatment than after oral administration. The excretion of 4 benzo[a]pyrene metabolites, including 3-OH-benzo[a]pyrene, is faster after oral administration. The percutaneous absorption of small doses of benzo[a]pyrene appears to be greater than the oral absorption.

Animals↗

Synthesis of a novel fluorinated benzo[a]pyrene: 4,5-difluorobenzo[a]pyrene.

The synthesis of 4,5-difluorobenzo[a]pyrene, as a fluorinated probe to investigate the involvement of the K-region in the further metabolic activation of benzo[a]pyrene metabolites, is described. Benzo[a]pyrene-4,5-dione obtained from 2,3-dichloro-5,6-dicyano-1,4-benzoquinone oxidation of cis-4,5-dihydro-4,5-dihydroxybenzo[a]pyrene was fluorinated with dimethylaminosulfur trifluoride to give 4H,5H,4,4,5,5,-tetra-fluorobenzo[a]pyrene. Defluorination using lithium aluminum hydride in tetrahydrofuran gave 4,5,-difluorobenzo[a]pyrene.

Benzo(a)pyrene↗

Induction of chromosomal aberrations and spindle disturbances in Chinese hamster epithelial liver cells in culture by pyrene and benzo[a]pyrene quinones.

Regioisomers of pyrene and benzo[a]pyrene quinones were tested for their ability to induce structural and numerical aberrations and spindle disturbance in Chinese hamster epithelial liver (CHEL) cells in culture. All quinones tested were clastogenic. Pyrene-1,8-quinone (P-1,8-Q) and benzo[a]pyrene-3,6-quinone (BP-3,6-Q) induced strikingly high levels of triradials. In addition, dicentrics and ring chromosomes were very common in BP-3,6-Q-treated cultures. Isomers of these compounds, pyrene-1,6-quinone (P-1,6-Q) and benzo[a]pyrene-1,6-quinone (BP-1,6-Q), induced unobtrusive patterns of chromosomal aberrations. We suspect that the P-1,8-Q and BP-3,6-Q moieties bound to the DNA were still reactive, and formed crosslinks and/or underwent redox cycling leading to high local concentrations of reactive oxygen species. In addition, P-1,8-Q and BP-3,6-Q induced c-mitoses, hyperdiploidies and polyploidies, in particular endoreduplications. These effects were not seen with the other two test compounds, or they were only detected at the highest concentrations used, which were strongly cytotoxic (c-mitoses with P-1,6-Q, polyploidies with BP-1,6-Q).

Animals↗