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The effect of norharman on the metabolism of benzo[alpha]pyrene by rat-liver microsomes in vitro in relation to its enhancement of the mutagenicity of benzo[alpha]pyrene.

The effect of norharman on the metabolism of benzo[alpha]pyrene by rat-liver microsomes was studied. Separation of the metabolites into hydrophilic and hydrophobic fractions showed that norharman inhibited the conversion of hydrophobic metabolites to hydrophilic ones. Analysis of the hydrophobic metabolites by high-pressure liquid chromatography showed that norharman also inhibited the disappearance of benzo[alpha]pyrene itself. However, large amounts of hydrophobic metabolites, such as phenol, quinones and diols, were formed in the presence of norharman, and formation of the strong mutagen 7,8-dihydroxybenzo[alpha]pyrene was increased 10-fold by norharman. The increase in formation of this compound may be one of the chief reasons why norharman enhances the mutagenicity of benzo[alpha]pyrene on Salmonella typhimurium.

Alkaloids

Regio- and stereoselectivity of various forms of purified cytochrome P-450 in the metabolism of benzo[a]pyrene and (-) trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene as shown by product formation and binding to DNA.

Highly purified cytochromes P-450(LM2) and P-450(LM4) and partially purified P-450(LM1), P-450(LM3b), and P-450(LM7) from rabbit liver microsomes exhibit different catalytic activities in the metabolism of benzo[a]pyrene (BzP) and (-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene [(-)trans-7,8-diol] in a reconstituted enzyme system. The two highly purified cytochromes also exhibit differences in the activation of BzP and (-)trans-7,8-diol to intermediates that bind to DNA, as well as in the stereoselective conversion of (-)trans-7,8-diol to the highly mutagenic and carcinogenic diol-epoxides r-7,t-8-dihydroxy-t-9,10-oxy-7,8,9,10- tetrahydrobenzo[a]pyrene (diol-epoxide I) and r - 7,t - 8 - dihydroxy - c - 9,10 - oxy - 7,8,9,10 - tetrahydrobenzo[a]pyrene (diol-epoxide II). P-450(LM2) is more active than P-450(LM4) in the metabolism of BzP and in its conversion to products that bind to DNA. In contrast, P-450(LM4) is more active than P-450(LM2) in the metabolism of (-)trans-7,8-diol and in its conversion to products that bind to DNA. The ratio of activity (percent substrate metabolized) with BzP relative to that with (-)trans-7,8-diol is 21 for P-450(LM2) and 0.3 for P-450(LM4); P-450(LM1), P-450(LM3b), and P-450(LM7) gave intermediate ratios. Marked stereoselectivity in the oxygenation of the (-)trans-7,8-diol to the highly mutagenic and putatively carcinogenic diol-epoxides I and II was observed with P-450(LM4), whereas the other preparations showed less selectivity. The ratio of diolepoxide I to diol-epoxide II ranges from 0.3 for P-450(LM7) to 11 for P-450(LM4). The substrate specificity and regio- and stereo-selectivity of the different forms of cytochrome P-450 may regulate the balance between activation and detoxification pathways of BzP and therefore determine the susceptibility of individual tissues, strains, and species to the carcinogenic action of BzP.

Animals

The benzo(alpha)pyrene deoxyribonucleoside products isolated from DNA after metabolism of benzo(alpha)pyrene by rat liver microsomes in the presence of DNA.

Rat liver microsomes (induced by 3-methylcholanthrene) were used to catalyze the binding of tritium-labeled benzo(alpha)pyrene to DNA. Enzymic degradation of this DNA to deoxyribonucleosides, followed by separation of the products by Sephadex LH20 column chromatography, revealed two major products. One of these was shown to be the same as that obtained from DNA with benzo(alpha)pyrene bound following treatment of mouse embryo cells in culture with the carcinogen. Neither product resembled those obtained from DNA that had been caused to react with benzo(alpha)pyrene 4,5-oxide (K-region eposide). The aryl hydrocarbon hydroxylase activity of the microsome preparations was determined and related to the extent of microsome-catalyzed hydrocarbon binding. Inhibitors of the enzyme epoxide hydrase increased this binding but caused the loss of one of the two major products. On the basis of the results obtained, a model is proposed of the mechanism of benzo(alpha)pyrene metabolism and DNA binding.

Aryl Hydrocarbon Hydroxylases

Tumorigenicity studies with diol-epoxides of benzo(a)pyrene which indicate that (+/-)-trans-7beta,8alpha-dihydroxy-9alpha,10alpha-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene is an ultimate carcinogen in newborn mice.

The tumorigenic activities of benzo(a)pyrene(BP), (+/-)-trans-7beta,8alpha-dihydroxy-9beta,10beta-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene (diol-epoxide 1), (+/-)-trans-7beta,8alpha-dihydroxy-9alpha,10alpha-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene (diol-epoxide 2), (+/-)-trans-7,8,-dihydroxy-7,8-dihydrobenzo(a)pyrene (BP 7,8-dihydrodiol), and the tetraols derived from the hydrolysis of diol-epoxide 2 were evaluated in newborn mice. The mice were given injections sequentially of 4, 8, and 16 nmoles of each compound on the first, eighth, and fifteenth days of life, and the animals were killed when they were 28 weeks old. Diol-epoxide 1 was highly toxic in newborn mice, and most of the animals treated with this compound died before weaning. Diol-epoxide 2 and BP 7,8-dihydrodiol were, respectively, about 40- and 15-fold more active than BP in causing pulmonary adenomas. Vehicle-treated control animals had an average of 0.13 lung adenoma/mouse, whereas animals treated with BP, BP 7,8-dihydrodiol, or diol-epoxide 2 had, respectively, 0.24, 1.77 and 4.42 pulmonary adenomas/mouse. Diol-epoxide 1 and the tetraols derived from diol-epoxide 2 did not induce pulmonary adenomas. The inactivity of diol-epoxide 1 under the conditions of our study should be interpreted with caution because of the high toxicity of this compound. The results of our study provide evidence that BP 7,8-dihydrodiol is a proximate carcinogenic metabolite and that diol-epoxide 2 is an ultimate carcinogenic metabolite of BP in the newborn mouse.

Adenoma

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

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

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

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

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

[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

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

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

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

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

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

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

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

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