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PubMed1977

[Transplacental effect of benz(a)pyrene and pyrene].

The transplacental and direct effect of benzo(a)pyrene (BP) and pyrene on A and C57BL mice and their offspring was studied. BP proved to present blastomogenic danger for the offspring. In A mice offspring the greatest blastomogenic effect was expressed with the dose of 6 mg: lung tumours developed in 76.8% against 12.3% in the control (P less than 0,001). Tumours of the liver were revealed in the offspring of C57BL mice, chiefly in males. Their incidence with the dose of 12 mg of BP was 31.6% in males: and 9.1% in female; in the controls--1.2% in males, in the control females no tumours of the liver were observed. Noncarcinogenic analogue of BP--pyrene produced no blastomogenic effect.

Adenoma↗

PubMed1986

Effect of aliphatic amides on oncogenic transformation, sister chromatid exchanges, and mutations induced by cyclopenta[cd]-pyrene and benzo[a]pyrene.

We examined the effects of the aliphatic amides isopropyl-valeramide (IVA) and allylisopropylacetamide (AIA) on oncogenic transformation and sister chromatid exchanges (SCE) induced by cyclopenta[cd]pyrene (CPP) and benzo[a]pyrene (B[a]P) in C3H/10T1/2 cells and on B[a]Pdiol-epoxide (BPDE)-induced mutation at the HGPRT locus in Chinese hamster ovary (CHO) cells. IVA and AIA significantly suppressed B[a]P and CPP transformation in vitro. Both amides were effective when given just prior to, simultaneously with, or 24 h after carcinogen exposure. On the other hand, IVA and AIA did not affect cytotoxicity, the frequencies of SCE induced by CPP or B[a]P, nor BPDE-induced mutations in CHO cells. These and previous results suggest that the mechanism of inhibition of transformation by IVA or AIA may be very specific and probably not related to the early initiation event in oncogenic transformation in vitro.

7,8-Dihydro-7,8-dihydroxybenzo(a)pyrene 9,10-oxide↗

PubMed1976

The role of 9-hydroxybenzo(a)pyrene in the microsome mediated binding of benzo(a)pyrene to DNA.

A study of the liver microsome-mediated binding to added DNA of the phenol metabolites of benzo(a)pyrene (BP-OH) and of 7,8-dihydro-7,8-dihydroxybenzo(a)pyrene (BP-7,8-diol) suggested that as in the case of BP itself the reaction was catalysed by the enzyme aryl hydrocarbon hydroxylase. The addition of glutathione to the microsomal incubation inhibited the binding of BP and BP-OH more than that of BP-7,8-diol. Analysis by LH20 chromatography of the deoxyribonucleoside products from BP-DNA showed greater inhibition by glutathione of formation of the major product believed to result from further metabolism of BP-OH, than of the product arising by metabolism of BP-7,8-diol. The chromatographic behaviour and fluorescence spectrum of this major product were consistent with its derivation from 9-hydroxybenzo(a)pyrene (BP-9-OH) and furthermore suggested that BP-9-OH-4,5-oxide was the derivative whose reaction with DNA yielded this microsome-mediated BP-DNA product.

Alkylation↗

PubMedDate not supplied

Metabolism and mutagenicity of dibenzo[a,e]pyrene and the very potent environmental carcinogen dibenzo[a,l]pyrene.

Dibenzo[a,l]pyrene (DB[a,l]P) is one of the most potent carcinogens ever tested in mouse skin and rat mammary gland. DB[a,l]P is present in cigarette smoke and, presumably, in other environmental pollutants. Metabolism and mutagenicity studies of this compound compared to the weak carcinogen dibenzo[a,e]pyrene (DB[a,e]P) can provide preliminary evidence on its mechanism of carcinogenesis. The mutagenicity of DB[a,l]P, DB[a,e]P, and benzo[a]pyrene (BP) was compared in the Ames assay with Aroclor-induced rat liver S-9. BP was the strongest mutagen. In strain TA100, DB[a,l]P and DB[a,e]P were marginally mutagenic. In strain TA98 both compounds were mutagenic, and DB[a,l]P induced more than twice as many revertants as DB[a,e]P. The mutagenicity of DB[a,l]P does not correlate with its carcinogenicity, since DB[a,l]P is a much stronger carcinogen, but a much weaker mutagen, than BP. The NADPH-supported metabolism of DB[a,e]P and DB[a,l]P was conducted with uninduced and 3-methylcholanthrene-induced rat liver microsomes. Metabolites were analyzed by reverse-phase HPLC and identified by NMR, UV, and mass spectrometry. Uninduced microsomes produced only traces of metabolites with either compound. The major metabolites of DB[a,l]P with induced microsomes were DB[a,l]P 8,9-dihydrodiol, DB[a,l]P 11,12-dihydrodiol, 7-hydroxyDB[a,l]P, and a DB[a,l]P dione. The metabolites of DB[a,e]P with induced microsomes were DB[a,e]P 3,4-dihydrodiol, 3-hydroxyDB[a,e]P, 7-hydroxyDB[a,e]P, and 9-hydroxyDB[a,e]P. Some of these metabolites are very useful in assessing possible pathways of activation in the initiation of cancer.

Animals↗

PubMed1978

Effects of administration to mice of butylated hydroxyanisole by oral intubation on benzo[a]pyrene-induced pulmonary adenoma formation and metabolism of benzo[a]pyrene.

Administration of butylated hydroxyanisole (BHA) by oral intubation 4 hours before challenge with benzo[a]pyrene (BP) inhibited the formation of pulmonary adenomas in A/HeJ mice. Incubation of BP with liver microsomes from mice that received BHA 2,4, or 8 hours before being killed resulted in less binding of BP metabolites to added DNA than occurred with control microsomes. High-pressure liquid chromatography studies of the BP metabolite pattern produced by the incubation of BP with liver microsomes from mice given BHA by oral intubation showed a decrease in formation of BP-4,5-oxide and 9-hydroxybenzo[a]pyrene. In contrast, the formation of 3-hydroxybenzo[a]-pyrene was increased. The was increased. The short interval between the administration of BHA by oral intubation and the observed biochemical changes indicated that BHA could exert a direct effect on the microsomal metabolism of BP. These changes in metabolism of BP occurred under conditions of BHA administration that produced a decreased neoplastic response to this carcinogen.

Adenoma↗

PubMed1975

Comparison of the cellular DNA-bound products of benzo(alpha)pyrene with the products formed by the reaction of benzo(alpha)pyrene-4,5-oxide with DNA.

DNA isolated from mouse embryo cell cultures that had been treated with [3H]benzo(alpha)pyrene was degraded with enzymes to deoxyribonucleosides, and the hydrocarbon-deoxyribonucleoside products were isolated by chromatography on a Sephadex LH20 column eluted with a water: methanol gradient. The hydrocarbon-deoxyribonucleoside products were not identical to those found in similar chromatograms of enzyme digests of DNA that had been reacted with benzo(alpha)pyrene-4,5-oxide in aqueous ethanol solution. This finding suggests that the metabolic activation of benzo(alpha)pyrene that results in this hydrocarbon becoming covalently bound to DNA in mouse embryo cells in culture may be more complex than simply formation of a K-region epoxide and reaction of that compound with the cellular DNA.

Animals↗

PubMed1979

Carcinogenicity of 2-hydroxybenzo(a)pyrene and 6-hydroxybenzo(a)pyrene in newborn mice.

Benzo(a)pyrene (BP), 2-hydroxybenzo(a)pyrene (2-HOBP), and 6-hydroxybenzo(a)pyrene (6-HOBP) were tested for tumorigenicity by i.p. injection into newborn mice. The mice were treated sequentially with 200, 400, and 800 nmol of compound on the first, eighth and fifteenth day of life, and the animals were killed at 24 weeks of age. Treatment with 2-HOBP caused about 4-fold more pulmonary tumors than BP, while 6-HOBP had little or no tumorigenic activity. Newborn mice treated with 2-HOBP, BP, and 6-HOBP had a 98, 81, and 11% incidence of pulmonary adenomas with an average of 24, 6.4, and 0.11 adenomas per mouse, respectively. In the control group, 7.5% of the animals had pulmonary adenomas with an average of 0.08 adenoma per mouse. When 25, 50, or 100 nmol of BP or 2-HOBP was applied to mouse skin once every 2 weeks for 60 weeks, both compounds had about the same carcinogenic activity. These results demonstrate the importance of evaluating the carcinogenic potential of chemicals in more than one tumor system. BP and 2-HOBP were tested for mutagenicity towards two strains of Salmonella typhimurium and towards Chinese hamster V79 cells in the presence of hepatic microsomes from rats pretreated with Aroclor 1254. The products formed during the metabolism of 2-HOBP or BP by liver microsomes had significant mutagenic activity.

Adenoma↗

PubMed1989

Metabolism of benzo[a]pyrene and 7 beta,8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10-tetrahydrobenzo[a pyrene in lung and liver of newborn mice.

Although the newborn mouse has been extensively used to test the tumorigenic activities of polynuclear aromatic hydrocarbons and their diol epoxide metabolites, no information is available on their metabolism in the newborn mouse in vivo. Therefore, we have investigated the metabolism and distribution of [3H]benzo[a]pyrene ([3H]BaP) and (+/-)-7 beta,8 alpha-[3H]dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9, 10-tetrahydrobenzo[a]pyrene ([3H]BPDE) in liver and lung of mice given i.p. injections of these compounds on their 1st, 8th and 15th days of life. In lung, identified metabolites of [3H]BaP included diols, quinones, and phenols. Their levels were higher on the 1st day compared to the 8th and 15th days of life. The pattern of organic extractable metabolites detected in mouse liver was different from that in lung, being dominated by unidentified polar metabolites, the levels of which increased with age. Levels of [3H]BPDE in liver and lung were measured by trapping with 2-mercaptoethanol. It was demonstrated that [3H]BPDE rapidly reaches the lung after i.p. injections. The half-lives of [3H]BPDE in lung and liver were similar to those observed in vitro. The results are discussed with respect to the known tumorigenic activities of BaP and BPDE in newborn mice and in mouse skin.

7,8-Dihydro-7,8-dihydroxybenzo(a)pyrene 9,10-oxide↗

PubMed1983

Syncarcinogenic effect of the environmental pollutants cyclopenteno[cd]pyrene and benzo[a]pyrene in mouse skin.

Benzo[a]pyrene (BP) and cyclopenteno[cd]pyrene (CPEP) are widespread environmental pollutants. CPEP is a relatively potent carcinogen in mouse skin with an activity second only to BP among environmental aromatic hydrocarbons. We have studied the combined application of BP and CPEP on mouse skin to determine their possible synergistic carcinogenic effect. Nine-week-old female Swiss mice in groups of 30 were treated on the back with high (H), medium (M) and low (L) doses, respectively, of 20 (H), 6.6 (M) or 2.2 (L) nmol BP or 200 (H), 66.6 (M) or 22.2 (L) nmol CPEP in 50 microliters acetone twice weekly for 48 weeks. Other groups received BP-H + CPEP-H, BP-M + CPEP-M, BP-L + CPEP-L, BP-H + CPEP-L, BP-M + CPEP-L, BP-L + CPEP-H, or BP-L + CPEP-M. A significant, 3- to 7-fold syncarcinogenic effect occurred when BP-M + CPEP-M were administered together. A smaller, but significant, synergistic effect (1.2- to 3.8-fold) was also observed when BP-M + CPEP-L or BP-L + CPEP-M was applied. Because of the syncarcinogenic effect of BP and CPEP, their abundance in engine emissions and ambient air samples may present a major source of carcinogenic risk.

Animals↗

PubMed1988

Dose-response relationships of the tumorigenicity of cyclopenta[cd]pyrene, benzo[a]pyrene and 6-nitrochrysene in a newborn mouse lung adenoma bioassay.

Cyclopenta[cd]pyrene (CPP) was a potent tumorigen when tested over a 5-fold dose range in the newborn mouse assay. A 20-fold increase in lung tumor multiplicity and a nearly 8-fold increase in tumor incidence was observed at the lowest total dose tested (1.55 mumol) with the dose-response relationship indicating a saturation of tumor multiplicity at approximately 7 tumors/animal. No liver nodules or lymphatic system tumors were noted. Analysis of dose-response data for benzo[a]-pyrene (BaP) and 6-nitrochrysene (6-NC) showed that tumor multiplicity for BaP also saturated at approximately 7 tumors/animal, whereas no similar saturation was found for 6-NC at up to 40 tumors/animal. Progression of lung adenomas to adenocarcinomas, as measured by the incidence of mice bearing malignant tumors, was essentially a linear function of dose. To facilitate comparison and maximize quantitative data obtainable from the newborn mouse assay-parameters were defined for tumor incidence (ED50), tumor multiplicity (TM1.0) and tumor malignancy (malignancy index). Values for the ED50 and TM1.0 were similar for the same compound and a tumorigenic potency series of 6-NC greater than BaP greater than CPP was obtained corresponding to a ratio of approximately 1:10-25:76.5-135, respectively. The malignancy index, however, indicated increased adenocarcinoma induction in the order CPP greater than 6-NC greater than BaP as expressed by the ratio 1:1.4:8.3, respectively.

Adenoma↗

PubMed1988

Differences in the DNA adducts formed in cultured rabbit and rat dermal fibroblasts by benzo(a)pyrene and (-)benzo(a)pyrene-7,8-diol.

Benzo(a)pyrene (BaP) is highly carcinogenic in rats but is without effect in rabbits when administered s.c. The possibility that BaP-DNA adducts could be responsible for this species difference was investigated by comparing BaP-deoxyribonucleoside adducts formed in dermal fibroblast cultures from Wistar rats and New Zealand rabbits. Treatment with [G-3H]BaP (1.2 microM) for 6, 24, and 48 h produced an essentially qualitative species-specific difference. Over 95% of the DNA adducts in the rabbit dermal cell cultures were derived from anti-BaPDE; the major BaP adduct formed (90%) was (+)-anti-BaPDE-deoxyguanosine. This adduct was formed at very low levels in the rat dermal fibroblasts (7%). These cells contained a large proportion of (+/-)-r-7,t-8-dihydroxy-c-9,10-oxy-7,8,9,10-tetrahydrobenzo(a)pyrene (syn-BaPDE)-DNA adducts (45%) and over 48% of other, unidentified, BaP-DNA adducts. Cells treated with (-)-BaP-7,8-diol (1.2 microM) produced almost exclusively (greater than 99%) (+)-anti-BaPDE-deoxyguanosine in rabbit cells, while the rat cells did not form this product. These results suggest that adducts other than anti-BaPDE-deoxyguanosine may be involved in rat s.c. BaP carcinogenesis; the preferential formation of (+)-anti-BaPDE-deoxyguanosine by rabbit dermal fibroblasts does not directly correlate with the resistance of rabbit dermis to tumor formation.

7,8-Dihydro-7,8-dihydroxybenzo(a)pyrene 9,10-oxide↗

PubMed1988

Synchronous fluorescence spectrophotometry of benzo[a]pyrene diol epoxide-DNA adducts: a tool for detection of in-vitro and in-vivo DNA damage by exposure to benzo[a]pyrene.

We have applied synchronous fluorescence spectrophotometry (SFS) to study benzo[a]pyrene diol epoxide (BPDE)-DNA adducts in biological samples. Adducts are measured as benzo[a]pyrene (BP) tetrols after acid hydrolysis, and give a peak at 374 nm of emission with a 34-nm wavelength difference. In vitro and in animal studies, there is a positive correlation between the amount of adducts and the BP dose. In cell culture studies, the amount of adducts is increased by increasing both the dose of BP and the time of culture with BP. In preliminary human studies, BPDE-DNA has been found by SFS in placental DNA from some but not all smoking mothers and in blood cell DNA from some individuals in occupationally exposed groups.

7,8-Dihydro-7,8-dihydroxybenzo(a)pyrene 9,10-oxide↗

PubMed1981

Synergistic, additive, and antagonistic mutagenic responses to binary mixtures of benzo(a)pyrene and benzo(e)pyrene as detected by strains TA98 and TA100 in the Salmonella/microsome assay.

Binary mixtures of benzo(a)pyrene (B(a)P) and benzo(e)pyrene (B(e)P) produce synergistic mutagenic (comutagenic) responses in Salmonella typhimurium strain TA98 (a frameshift detector). The optimum enhancement (25 X) was found at B(a)P concentration of 0.3 microgram/plate and B(e)P concentration of 1.5 microgram/plate. The response of strain TA100 (mostly a base-substitution detector) is opposite that of TA98, showing antagonism and additivity in similar concentration ranges.

Benzo(a)pyrene↗

PubMedDate not supplied

Stereoselective metabolism of benzo[a]pyrene and 7-methylbenzo[a]pyrene by liver microsomes from sprague-Dawley rats pretreated with polychlorinated biphenyls.

The dihydrodiols formed from the metabolism of benzo[a]pyrene (BaP) and 7-methylbenzo[a]pyrene (7-MBaP) by liver microsomes from male Sprague-Dawley rats treated with polychlorinated biphenyls (PCBs, Aroclor 1254) have been examined by circular dichroism (CD) spectropolarimetry. Comparisons with optically pure enantiomers obtained via high performance liquid chromatography (HPLC) resolution of diastereomeric di-(-)-menthoxyacetates indicated that the trans-4,5-, 7,8- and 9,10-dihydrodiols formed from BaP metabolism are predominantly R,R-enantiomers with optical purities greater than 98%. The major enantiomers of the metabolically formed 7-MBaP-trans-4,5- and 9,10-dihydrodiols and 7-hydroxymethyl-BaP-trans-9,10-dihydrodiol have Cotton effects very similar to those of BaP-4R,5R- and 9R,10R-dihydrodiols, respectively. These 7-MBaP-trans-4,5- and 9,10-dihydrodiol metabolites therefore contain predominantly the R,R-enantiomers. The optical purity of metabolically formed 7-MBaP-trans-4,5-dihydrodiol was determined to be 30.8% enriched in (-)-enantiomer. The optical purity of the 9,10-dihydrodiol was not determined due to the lack of synthetic standards. The major trans-7,8-dihydrodiol enantiomer formed from 7-MBaP metabolism is a (+)-enantiomer (optical purity 60.4%) which has Cotton effects opposite in sign to that of the (-)-7R,8R-dihydrodiol formed from BaP metabolism. The results indicate that a methyl substituent on a polycyclic aromatic hydrocarbon may alter the stereoselective properties of the microsomal drug-metabolizing enzyme systems toward the substrate molecule.

Animals↗

PubMed1986

Excretion of benzo[a]pyrene-Gua adduct in the urine of benzo[a]pyrene-treated rats.

A benzo[a]pyrene(BP)-Gua adduct was extracted in the urine of rats treated with BP. Some (0.15%) of the administered dose of BP was excreted as BP-Gua within 48 h. A double labelling experiment demonstrated that the excreted product contained both a BP and a Gua moiety. Partially hepatectomized rats treated with [14C]Gua during the regenerative phase were injected with [3H]BP and the urine collected and processed by chromatographic procedures. The adduct had similar chromatographic properties to the adduct released from human PLC/5 cells treated with 7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BPDE) and co-chromatographed with 7-BPDE-Gua released from BPDE-adducted DNA under aqueous conditions. Detection and quantitation of BP-Gua offers an alternative, non-invasive method of monitoring individuals exposed to carcinogenic polycyclic aromatic hydrocarbons (PAHs).

Animals↗

PubMed1989

Benzo[a]pyrene-DNA-adducts and monooxygenase activities in mice treated with benzo[a]pyrene, cigarette smoke or cigarette smoke condensate.

Synchronous fluorescence spectrophotometry (SFS), developed to study benzo[a]pyrene-7,8-diol-9,10-epoxide(BPDE)-DNA, was used to measure the in vivo formation of DNA-adducts in genetically responsive C57BL/6 (B6) and non-responsive DBA/2 (D2) mice. Treatment with cigarette smoke by inhalation for 3-16 days, or i.p. injection of cigarette smoke condensate or neutral fraction did not lead to detectable levels of BPDE-DNA-adducts in either lungs or liver, although aryl hydrocarbon hydroxylase (AHH) activity, an indicator of benzo[a]pyrene (BP) metabolism, was clearly induced in lungs of B6 mouse. A dose-dependent amount of BPDE-DNA-adducts in lung and somewhat less in liver was found after i.p. injection with BP (20-80 mg/kg). Mice treated with vehicle or 4 mg/kg of BP were negative for adducts by SFS. In B6 mice AHH was induced both in lungs and livers while there was no AHH induction in D2 mice although the levels of BPDE-DNA-adducts were somewhat higher than in B6 mice. Thus, no clear correlation seems to exist between AHH activity and the formation of BPDE-DNA-adducts. Also, according to our results SFS can be used to quantitate adduct-formation in in vivo animal studies.

7-Alkoxycoumarin O-Dealkylase↗

PubMed1990

Metabolism of benzo[a]pyrene and (-)-trans-benzo[a]pyrene-7,8-dihydrodiol by freshly isolated hepatocytes of brown bullheads.

The metabolism of [3H]benzo[a]pyrene (BP) and (-)-trans-[14C]7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (BP-7,8-diol) was studied in freshly isolated hepatocytes of the wild benthic fish, brown bullhead (Ictalurus nebulosus). Bullhead hepatocytes incubated with 40 microM [3H]BP for 1 h metabolized BP to water soluble metabolites which were separated on silica gel t.l.c. plates to reveal conjugates with glucuronic acid, glutathione, and sulfate (51%, 14% and 4% of total metabolites, respectively). Additional metabolites that were extractable with ethyl acetate were separated by reversed phase HPLC to reveal only two major metabolites: BP-9,10-dihydrodiol and BP-7,8-diol (13% and 2.6% of total metabolites, respectively). Hepatocytes isolated from individual fish displayed an 11-fold variability in the rates at which they metabolized BP (756 +/- 167 pmol x mg dry wt-1 x h-1), which correlated negatively (r = -0.7, P less than 0.01) with an 18-fold variability in the glycogen content of the cells. Hepatocytes isolated from the same fish, in parallel incubations under the same optimum conditions, metabolized BP-7,8-diol 4.5-fold faster than they metabolized BP. The variability in the rate of BP-7,8-diol metabolism was about 7-fold. Major metabolites included glutathione conjugates, glucuronides and sulfates (35%, 25% and 30% of total metabolites, respectively). These conjugates, like those formed from BP, were degradable with gamma-glutamyltransferase, beta-glucuronidase and arylsulfatase, respectively. Ethyl acetate extractable metabolites were predominantly isomeric benzo-ring tetrahydrotetrols (9% of total metabolites). In summary, this study indicates that during short-term incubations bull-head hepatocytes metabolize BP and BP-7,8-diol primarily to conjugated derivatives. The usefulness of thin-layer chromatography for the convenient determination of the rate of BP-7,8-diol metabolism is demonstrated.

Animals↗

PubMed1987

Modulation of the cytotoxicity and mutagenicity of benzo[a]pyrene and benzo[a]pyrene 7,8-diol by glutathione and glutathione S-transferases in mammalian cells (CHO/HGPRT assay).

Biologically reactive metabolites of benzo[a]pyrene (BP) and benzo[a]-pyrene 7,8-diol (BP-diol), formed by the mixed-function oxidase (MFO) system, are substrates for conjugation and detoxication by glutathione (GSH) when catalyzed by glutathione S-transferases (GSHT). We have investigated the detoxication of BP- and BP-diol-induced cytotoxicity and mutagenicity with GSH by supplementing the S9 mix used in the Chinese hamster ovary cells/hypoxanthine-guanine phosphoribosyltransferase (CHO/HGPRT) assay with GSH (6.5 mM) or GSH plus GSHT. The addition of GSH to the S9 mix resulted in a reduction of BP- and BP-diol induced cytotoxicity. GSH plus GSHT eliminated BP-induced cytotoxicity and reduced the mutagenicity of BP. GSH inhibited the mutagenicity at low (essentially non-lethal) concentrations of BP-diol, but did not do so at toxic concentrations. GSH plus GSHT inhibited the cytotoxicity and mutagenicity of BP-diol at concentrations not affected by GSH alone. These studies indicate that biochemical mechanisms of detoxication can affect the biological activity of a carcinogen, such as BP or BP-diol as profoundly as bioactivation by the MFO system.

Animals↗