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PubMed1991

Micronuclei in mouse skin cells following in vivo exposure to benzo[a]pyrene, 7,12-dimethylbenz[a]anthracene, chrysene, pyrene and urethane.

Detection of micronuclei (MN) in skin cells from HRA/Skh hairless mice treated with chemical or physical agents may prove informative in qualitative and quantitative studies of skin carcinogenesis. MN induction and cell survival were estimated in cytokinesis-blocked keratinocytes, cultured for 4 days in vitro, after a single topical dose of various organic compounds. Treatment with 2.56 micrograms (10 nmol) 7,12-dimethylbenz[a] anthracene (DMBA) resulted in maximal MN induction in cells removed from skin 12-24 hr after topical administration (79-88 MN/1,000 cells compared with 10-16 MN/1,000 cells in acetone-treated controls). Even in cells removed only 1 hr after DMBA treatment, a significant increase in MN was evident. However, to allow sufficient time for metabolic activation, a sampling time for of 24 hr was adopted for all test substances. Dose-dependent increases in MN were observed with DMBA, benzo[a]pyrene, chrysene, and urethane. Increased numbers of micronucleated cells were detected at the lowest doses administered in the present study (0.128, 0.5, 50, and 50 micrograms, respectively). Although reduced cell recovery occurred following exposure of mice to acetone, pyrene, and other chemicals, there was no evidence that cytotoxicity contributed to MN scored in keratinocytes. Moreover, the probable noncarcinogen, pyrene, failed to induce MN at doses from 2.5 micrograms to 2.5 mg/mouse. These results show that it is possible to assess chemical exposure in skin by measuring cell survival and skin genotoxicity by measuring MN induction in cultured keratinocytes. The available data suggest that MN induction may be a useful indicator of the carcinogenic potential of chemicals applied to the skin.

9,10-Dimethyl-1,2-benzanthracene↗

PubMed1985

Effect of ellagic acid and hydroxylated flavonoids on the tumorigenicity of benzo[a]pyrene and (+/-)-7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene on mouse skin and in the newborn mouse.

Ellagic acid, quercetin and robinetin were tested for their ability to antagonize the tumor-initiating activity of benzo[a]pyrene (B[a]P) and (+/-)-7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (B[a]P 7,8-diol-9,10-epoxide-2), the ultimate carcinogenic metabolite of benzo[a]-pyrene. Ellagic acid, robinetin or quercetin (2500 nmol) had no tumor-initiating activity on mouse skin, but the topical application of 2500 nmol of ellagic acid 5 min before a tumor-initiating dose of 200 nmol of B[a]P 7,8-diol-9,10-epoxide-2 caused a 59-66% inhibition in the number of skin tumors per mouse that were observed after 15-20 weeks of promotion with 12-O-tetradecanoylphorbol-13-acetate. Similar treatment with 2500 nmol of robinetin or quercetin caused a statistically insignificant 16-24% inhibition in the tumor-initiating activity of 200 nmol of B[a]P 7,8-diol-9,10-epoxide-2 applied 5 min later. Treatment of mice with 2500 nmol of ellagic acid 5 min before the application of 50 nmol of B[a]P inhibited the mean number of skin tumors per mouse by 28-33% after 15-20 weeks of promotion, but these decreases were not statistically significant. Robinetin and quercetin had little or no effect on the tumor-initiating activity of B[a]P on mouse skin. Treatment of preweanling mice with 1/7, 2/7 and 4/7 of the total dose of ellagic acid (300 nmol), robinetin (1400 nmol), myricetin (1400 nmol) or quercetin (1400 nmol) i.p. on their first, eighth and fifteenth day of life, respectively, did not cause the formation of tumors in animals that were killed 9-11 months later. Similar treatment of preweanling mice with the above doses of the phenolic compounds 10 min before the i.p. injection of a total dose of 30 nmol of B[a]P 7,8-diol-9,10-epoxide-2 during the animal's first 15 days of life caused a 44-75% inhibition in the number of diol-epoxide-induced pulmonary tumors per mouse. Similar treatment with these plant phenols had little or no effect on B[a]P-induced pulmonary tumors.

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

PubMed1986

In vivo formation and persistence of DNA adducts in mouse and rat skin exposed to (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene and (+/-)-7 beta,8 alpha-dihydroxy-9 alpha,10 alpha-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene.

The in vivo DNA adduct formation of (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (BPD) and (+/-)-7 beta,8 alpha-dihydroxy-9 alpha,10 alpha-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BPDE) were compared and the persistence and disappearance of the adducts in both mouse and rat epidermis determined. BPD (100 nmol/mouse in 150 microliter acetone and 200 nmol/rat in 300 microliter acetone) and anti-BPDE (77 nmol/mouse in 150 microliter tetrahydrofuran and 154 nmol/rat in 300 microliter tetrahydrofuran) were topically applied to 50-day-old male Swiss mice and 35-day-old Wistar rats. To improve the identification of the DNA adducts formed, an acid hydrolysis technique was used to convert the BPD- and anti-BPDE-deoxyribonucleoside adducts formed in mouse and rat skin to BP tetrols. The modified deoxyribonucleosides and BP tetrols obtained by hydrolysis of adducts were isolated by reverse-phase h.p.l.c. At approximately similar doses per unit area of treated skin, the initial total binding of these compounds to epidermal DNA and the level of modified deoxyribonucleosides was approximately 6-fold lower in rat skin epidermis than in mouse skin epidermis. Similar ratios of (+/-)-anti-BPDE-deoxyguanosine (dGuo) to (+/-)-syn-BPDE-dGuo adducts (5.7 and 6.1, determined by h.p.l.c. analysis of BP tetrols obtained by hydrolysis of modified dGuo) were found in both mouse and rat epidermis a short time (6 h) after topical application of (+/-)-trans-BPD. Three hours after topical application of (+/-)-anti-BPDE, the ratios of BP-7,10/8,9-tetrol to 7/8,9,10-tetrol were 9:1 in mouse epidermal DNA and 6:1 in rat epidermal DNA. One and three weeks after application of these two compounds, only (+)-anti-BPDE-dGuo was detected in mouse epidermis; 2 and 0.2% of the initial (+)-anti-BPDE-dGuo level was found to persist in the epidermal DNA from BPD- and anti-BPDE-treated mice respectively. No DNA adducts were detected in rat epidermis 3 weeks after BPD and anti-BPDE treatment. Thus, 3 weeks after topical application of BPD and anti-BPDE to mouse and rat skin, the DNA adducts completely disappeared from rat epidermis while they persisted in mouse epidermis. The results suggest that: the persistence of (+)-anti-BPDE-dGuo may be related to carcinogenesis in mouse epidermis by BPD and anti-BPDE; the complete disappearance of the anti-BPDE-dGuo adduct may also account in part for the relative resistance of tissue from this species to the carcinogenic action of benzo[a]pyrene.

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

PubMed1987

In vitro inhibition of the metabolism and mutagenicity of benzo(a)pyrene and benzo(a)pyrene-7,8-dihydrodiol by naphthazarin and other naphthol derivatives.

Among naphthol derivatives tested in the Ames assay, 5,8-dihydroxy-1,4-naphthoquinone or naphthazarin was found to be the most effective inhibitor of benzo(a)pyrene mutagenicity. The inhibitory activity is due in part to the redox cycling of naphthazarin with the concommitant transfer of reducing equivalents from NADPH to molecular oxygen, thus diverting electrons from cytochrome P-450 enzymes. Metabolite separations showed a decrease in microsomal metabolism of benzo(a)pyrene and of benzo(a)pyrene-7,8-dihydrodoil upon addition of naphthazarin. Since both NADP and dicoumarol inhibited the naphthazarin-stimulated non-stoichiometric consumption of NADPH and oxygen then naphthazarin redox cycling probably involves both DT-diaphorase and NADPH cytochrome P-450 reductase.

Benzo(a)pyrene↗

PubMed1991

Determination of benzo[a]pyrene sulfate conjugates from benzo[a]pyrene-treated cells by continuous-flow fast atom bombardment mass spectrometry.

The level of certain water-soluble hydrocarbon conjugates, such as benzo[a]pyrene sulfates (BP-SO4), is a direct measure of carcinogenic polycyclic aromatic hydrocarbon metabolism and an indication of exposure. A new method, based on continuous-flow high-resolution fast atom bombardment mass spectrometry, has been developed for the analysis of BP-SO4 in the medium of cell cultures treated with benzo[a]pyrene. An organic solvent extract of medium from cultures of the human hepatoma cell line (HepG2) was fractionated by reversed-phase SEP-PAK chromatography and microbore high-performance liquid chromatography (HPLC). The HPLC fraction containing BP-SO4 was collected, dried, and injected into a stream of acetonitrile/water/glycerol that was continuously flowing to the tip of the sample probe which was being bombarded continuously by a beam of high-energy xenon atoms. Molecular anions of BP-SO4 (m/z 347) desorbed from the liquid were analyzed by a high-resolution (m/delta m 5000) mass spectrometer and recorded as a function of time. As little as 1.5 pg of BP-SO4 could be detected with a S/N ratio of 8. The mass spectrometer response was linear with respect to the quantity of BP-SO4 injected over the range from 15 to 625 pg. The results obtained with this method show that the HepG2 cultures metabolized 3% of the benzo[a]pyrene into the BP-SO4 conjugate in 24 h. This procedure, which was used to detect and quantify directly BP-SO4 in culture medium without the use of a radiolabeled precursor, should be generally applicable for analyses of sulfated conjugates resulting from the metabolism of different hydrocarbons.

Benzo(a)pyrene↗

PubMed1991

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

The metabolism of benzo[a]pyrene (B[a]P) and (-)-trans-benzo[a]pyrene-7,8-dihydrodiol [(-)-B[a]P-7,8-diol], a major putative proximate carcinogenic metabolite of B[a]P, was compared in freshly isolated hepatocytes from mirror carp, a strain of common carp (Cyprinus carpio, L.). Hepatocytes incubated with 40 microM [3H]B[a]P produced 1.22 nmol equivalents of B[a]P metabolites/mg dry wt of cells/h. Conjugated derivatives represented approximately 65% of all B[a]P metabolites and included glucuronides (38%), glutathione conjugates (21%) and sulfates (6%). About 14% of the total accumulated metabolites of B[a]P determined after 1 h incubations were identified as unconjugated derivatives, predominantly B[a]P-9,10-dihydrodiol and B[a]P-7,8-diol (7.4 and 3.1% of total metabolites respectively), with only traces of B[a]P tetrols (less than 1%). Hepatocytes incubated with 40 microM (-)-[14C]B[a]P-7,8-diol produced 4.78 nmol equivalents of metabolites/mg dry wt during a 1 h incubation, yielding an average rate of metabolism during this time period approximately 53% of that determined after a 5 min incubation. The profile of (-)-B[a]P-7,8-diol metabolites remained constant with incubation time (glucuronides, 30-33%; conjugates with glutathione, 43-46%; polyhydroxylated B[a]P derivatives plus sulfate conjugates, 22-24%). HPLC analysis revealed that polyhydroxylated metabolites amounted to 18% of the total metabolites; thus sulfate conjugates amounted to only 4% of the total metabolites. The trans-2 B[a]P-tetrol, which is the major hydrolysis product of (+)-anti-benzo[a]pyrene-7,8-diol-9,10-epoxide (anti-BPDE), represented approximately 11% of the accumulated metabolites of (-)-B[a]P-7,8-diol. Despite the much larger amounts of BPDE formed from (-)-B[a]P-7,8-diol than from B[a]P, the amounts of B[a]P equivalents covalently bound to cellular DNA were the same following 1 h incubations with either substrate (247 +/- 42 or 212 +/- 42 pmol/mg DNA respectively). Thus biochemical and physiological factors other than the production of BPDE are critically involved in determining the level of DNA adducts in hepatocytes as well as the role of these adducts in hepatocarcinogenesis.

Animals↗

PubMed1987

Glutathione depletion suppresses conjugation of benzo[a]pyrene metabolites and (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene metabolites with glutathione but does not affect their binding to DNA in C3H/10T1/2 mouse fibroblasts.

The study was aimed at determining the role of glutathione (GSH) conjugation in the binding of reactive benzo[a]pyrene (BaP) species to DNA of C3H/10T1/2 cells. In order to suppress GSH conjugation cells were depleted of GSH by treatment with buthionine sulfoximine for 18 h and 1-chloro-2,4-dinitrobenzene for 1 h prior to incubation with radiolabelled substrates. Under these conditions GSH levels decreased to less than 1% of the control value. C3H/10T1/2 cells produced GSH conjugates with 7,8-dihydroxy-9,10-oxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BaPDE) comprising 6% of the total metabolites formed from BaP or (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (BaP-7,8-diol). In GSH-depleted cells formation of GSH conjugates with metabolic products of BaP or BaP-7,8-diol was suppressed to 1% of total metabolites during an 8-h incubation period. Metabolic activation of BaP and BaP-7,8-diol by C3H/10T1/2 cells resulted in the formation of DNA adducts which largely consisted of BaPDE:deoxyguanosine. Depletion of GSH altered neither the degree of DNA binding nor the pattern of DNA adducts to any significant extent. When C3H/10T1/2 cells were co-incubated with microsomes from liver of 3-methylcholanthrene-treated rats for 1 h in order to activate BaP or BaP-7,8-diol extracellularly, the same pattern of GSH conjugates and DNA adducts was generated as by intracellular metabolism of the polycyclic hydrocarbons. No GSH conjugates were detected following co-incubation of microsomes with GSH-depleted C3H/10T1/2 cells. The formation of DNA adducts again remained unaffected by the suppression of conjugation. C3H/10T1/2 cells are apparently capable of conjugating BaPDE with GSH but are not capable of trapping by GSH conjugation those BaPDE moieties which bind to DNA. The results are compatible with the notion that BaPDE is partially contained in a cellular compartment--presumably the lipid environment of membranes--where it is inaccessible to GSH transferases of C3H/10T1/2 cells.

Animals↗

PubMed1987

Human hair follicle benzo[a]pyrene and benzo[a]pyrene 7,8-diol metabolism: effect of exposure to a coal tar-containing shampoo.

Assay systems for the evaluation of carcinogen interaction with human tissues are essential for assessing cancer risk. Hair follicles are a readily available source of human epithelial tissue and offer an excellent system with which to study carcinogen metabolism in human populations. In this study freshly plucked human hair follicles were employed to measure the metabolism of benzo[a]pyrene (BP), benzo[a]pyrene-7,8-diol (BP 7,8-diol), and the enzyme-mediated binding of [3H]-BP to DNA. The effect of human exposure to a crude coal tar (CCT)-containing shampoo, a preparation rich in polycyclic aromatic hydrocarbons (PAHs), on these parameters was also evaluated. Twelve healthy volunteers were studied before and after shampooing their hair daily for 4 days with the CCT-containing shampoo. Wide interindividual variation was observed in basal cytochrome P-450-dependent aryl hydrocarbon hydroxylase (AHH) activity which ranged from 0.6-17.6 fmol water-soluble BP metabolites/h/hair follicle (mean +/- SE of 32 individuals was 9.7 +/- 0.9). After use of the shampoo for 4 days AHH activity increased in 10 of the 12 volunteers (50-148%) and enhancement of enzyme-mediated binding of BP to DNA was detected in most subjects. Hair follicles were shown to convert BP to several metabolic species including BP 7,8-diol, a major precursor of the ultimate carcinogenic metabolite of BP. Benzo[a]pyrene-7,8-diol itself was also metabolized by the human hair follicles in this system. Clotrimazole, a known inhibitor of the metabolism of BP as well as the carcinogenicity of the hydrocarbon in rodent skin, was found to inhibit AHH and the in vitro metabolism of BP and BP 7,8-diol in human hair follicles. Oral administration of a similar antifungal imidazole, ketoconazole at a dose of 200 mg daily for 5 days, to healthy volunteers also resulted in greater than 90% inhibition of hair follicle AHH activity. These studies indicate that hair follicles represent an accessible tissue suitable for assessing the extent of PAH carcinogen metabolism in human subjects. Furthermore, enzyme activity critical to cancer induction by PAHs was shown to be inducible following the use of a CCT-containing shampoo. This carcinogen-activating enzyme system was substantially inhibited by imidazole compounds, suggesting that they may prove effective as anticarcinogens in human populations.

Aryl Hydrocarbon Hydroxylases↗

PubMed1985

Inhibition of benzo(a)pyrene and benzo(a)pyrene-trans-7,8-diol metabolism and DNA binding in mouse lung explants by ellagic acid.

The effect of ellagic acid, a naturally occurring plant phenol, on the binding to DNA and metabolism of benzo(a)pyrene (BP) and trans-7,8-dihydro-7,8-dihydroxybenzo(a)pyrene (BP 7,8-DHD) in cultured explants of strain A mouse lung was investigated. The explants were cultured in a rocking organ culture chamber for 16 h in the presence or absence of 10, 25, 50, and 100 microM ellagic acid. These concentrations of ellagic acid were nontoxic as determined by biochemical and histological methods. The ellagic acid was then removed from the cultures, and the explants were incubated with either 1 microM [3H]BP or [3H]BP 7,8-DHD for 24 h. Explant DNA was isolated using hydroxylapatite chromatography, and the BP metabolites in the medium were analyzed by high-pressure liquid chromatography. Ellagic acid (50 microM) inhibited the binding of BP and BP 7,8-DHD to lung DNA by 46 to 50% and 60 to 70%, respectively. High-pressure liquid chromatography analysis showed that ellagic acid (100 microM) inhibited the metabolism of BP by 20 to 40% and of BP 7,8-DHD by 20%, as indicated by the increased amounts of unmetabolized substrates and decreased amounts of metabolites in the medium. The major BP:DNA adduct in the explants was 7R-N2-[10 beta-[7 beta, 8 beta, 9 alpha-trihydroxy-7,8,9,10-tetrahydrobenzo(a)pyrene]yl: deoxyguanosine, and its formation was reduced by 60 to 65% in the presence of 100 microM ellagic acid. These data suggest that the reduction of BP and BP 7,8-DHD metabolite binding to DNA by ellagic acid may have been due to inhibition of the formation and/or removal of BP 7,8-diol-9,10-epoxide prior to its binding to DNA.

Animals↗

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↗

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↗