[CANCER RESEARCH 51, 5284-5291. October 1. 1991] Activation of Amino-a-carboline, 2-Amino-l-methyl-6-phenylimidazo[4,5-A]pyridine, and a Copper Phthalocyanine Cellulose Extract of Cigarette Smoke Condensate by Cytochrome P-450 Enzymes in Rat and Human Liver Microsomes1 Tsutomu Shimada2 and F. Peter Guengerich3 Department of Biochemistry and Center in Molecular Toxicology, Vanderbilt University School of Medicine, Nashville, Tennessee 37232-0146 ABSTRACT The ability of cigarette smoke condensate to induce a genotoxic re sponse has been measured in liver microsomal and reconstituted monooxygenase systems containing rat and human cytochrome P-450 (P-450) enzymes, as determined by unni gene expression in Salmonella typhimurium TA1535/pSK1002. The reactivities of amino-a-carboline and 2amino-l-methyl-o-phenylimidazo|4,5-A)pyridine (PhIP), two compounds known to be present at considerable levels in cigarette smoke condensate, were also determined and compared with regard to genotoxicity. Aminoa-carboline and PhIP are activated principally by P-450 1A2 enzymes in human and rat liver microsomes: (a) activation of both compounds was catalyzed efficiently by liver microsomes prepared from rats treated with 5,6-benzoflavone, isosafrole, or the commercial polychlorinated biphenyl mixture Aroclor 1254, and the activities could be considerably inhibited by antibodies raised against P-450 1A1 or l A2; (b) the rates of activation of these compounds were correlated with the amount of human P-450 1A2 and of phenacetin O-deethylation activity in different human liver microsomal preparations, and these activities were inhibited by anti-P450 l A2; (c) reconstituted enzyme systems containing P-450 1A enzymes isolated from rats and humans showed the highest rates of activation of amino-a-carboline and PhIP. In rat liver microsomes PhIP may also be activated by P-450 3A enzymes; activity was induced in rats treated with pregenenolone 16a-carbonitrile and was inhibited by anti-human P-450 3A4. However, in humans the contribution of P-450 3A enzymes could be excluded as judged by the very low effects of anti-P-450 3A4 on the microsomal activities and poor correlation with P-450 3A4-catalyzed activities in various liver samples. Cigarette smoke condensate strongly inhibited the activation of several potent procarcinogens by human liver microsomes, particularly the reactions catalyzed by P-450 1A2, but was not so inhibitory of the activation reactions catalyzed by P-450 3A4 and of P-450 2D6-catalyzed bufuralol I'-hydroxylation. Genotoxic compo nents of the cigarette smoke condensate were extracted by using copper phthalocyanine cellulose (blue cotton). Genotoxicity of this extract was observed only after activation by P-450, and the inhibition of P-450 l A2 activities by these extracts was slight. The following results collectively indicate that P-450 IA2 may be the major catalyst for the activation of the components in this blue cotton extract: (a) isosafrole and Aroclor 1254 induced the activities seen in rat liver microsomes; (b) in different human liver preparations the activation of the extract was correlated with activities catalyzed by P-450 1A2 and was inhibited by 7,8-benzoflavone or a human autoimmune antiserum that strongly and specifically recog nizes human P-450 1A2; (c) reconstituted systems containing purified human, rat, or rabbit P-450 1A2 catalyzed the activation of the extract. The participation of the human P-450 2D6 enzyme in the activation of these chemicals does not seem as likely because the activities were not inhibited by quinidine or by antibodies raised against rat P-450 2D1. Thus, the work does not provide evidence for the activation of genotoxic components of tobacco smoke by P-450 2D6 as being the basis for the reported association between debrisoquine 4-hydroxylation and incidence Received 4/4/91; accepted 7/19/91. The costs of publication of this article were defrayed in part by the payment of page charges. This article must therefore be hereby marked advertisement in accordance with 18 U.S.C. Section 1734 solely to indicate this fact. 1Supported in part by USPHS Grants CA 44353 and ES 00267 (F. P. G.) and by a Grant in Aid for Cancer Research from the Ministry of Education, Science, and Culture of Japan (T. S.). 2 Present address: Osaka Prefectura! Institute of Public Health, Nakamichi, Higashinari-ku. Osaka 537. Japan. 3 To whom requests for reprints should be addressed. of lung cancer. The present results show for the first time that cigarette smoke condensate contains both inhibitors of P-450 enzymes and procar cinogens capable of being activated by P-450 enzymes and that the P450 1A2 enzymes appear to be the most important catalysts for the (hepatic) activation reaction of a copper phthalocyanine cellulose extract of cigarette smoke condensate. INTRODUCTION A positive relationship between ingestion of tobacco smoke and cancers of the lung and other tissues has been established in epidemiological investigations; further, most cancer scien tists agree that approximately one-third of all cancers in the United States may be attributed to tobacco use (1,2). However, not all smokers acquire cancer and there is reason to believe that genetic factors are operative (2-4). Chemical carcinogens often produce their effects by modify ing DNA and causing tumor initiation (5). Indeed, there is a reasonable correlation between the carcinogenicity of chemicals and their mutagenicity in simple bacterial systems (6), at least in the absence of dramatic cell proliferation and tumor pro motion. Indeed, cigarette smoke condensate has been shown to be mutagenic after activation by rat liver microsomes (7) and direct mutagens are excreted in the urine of smokers (8). Ciga rette smoke and even tobacco itself are extremely complex mixtures and contain thousands of individual chemicals [>4000 have reportedly been identified (9)], many of which may have the capability to induce cancer. Exactly which chemicals in the tobacco and smoke are most responsible for causing cancer is unknown. Some classes of compounds under consideration are polycyclic aromatic hydrocarbons, arylamines, nitrosamines, vinyl monomers, radioisotopes, benzene, and catechols (9-12). The work of Kier et al. (7) suggests that P-4504 enzymes are involved in the activation of chemicals in cigarette smoke condensate to mutagens. However, there are many different P450 enzymes and most of these show rather independent pat terns of regulation and catalytic specificity (23, 24). Epidemi ological studies suggest that human P-450 1Al and P-450 2D6 may have roles in the etiology of tobacco-related cancer (25, 26). However, the complexity of the chemical mixtures in 4 The abbreviations used are: P-450, microsomal cytochrome P-450; BNF, ßnaphthoflavone (5,6-benzoflavone); ISF, isosafrole; PCN, pregnenolone-16n-carbonitrile: Aroclor, Aroclor 1254, a polychlorinated biphenyl mixture containing ~54% chlorine; A«C,amino-n-carboline; PhIP, 2-amino-l-methyl-6-phenylimidazo[4,5-e]pyridine; MelQ, 2-amino-3,5-dimethylimidazo[4,5-/]quinoline; IQ, 2amino-3-methylimidazo[4,5-/]quinoline; 6-AC, 6-aminochrysene. The P-450 en zymes characterized in this laboratory are sometimes referred to with abbrevia tions based upon the substrates which were utilized during purification. See Nebert et al. (13) for a categorization of the P-450 genes and Guengerich (14) for a review of individual human P-450 enzymes; both references describe related preparations derived in other laboratories. For reference, P-450 3A4 (P-450NF>is the nifedipine oxidase (15-17), P-450 2D6 (P-450DB) is the debrisoquine 4hydroxylase/bufuralol l'-hydroxylase (18), P-450 1A2 (P-450PA) is the highaffinity phenacetin O-deethylase (18, 19), and P-450MP refers to a group of enzymes (P-450MP.„P-450MP-2,P-450MP.j, P-450TB: CYP 2C8, CYP 2C9, CYP 2C10, and other genes in the 2C family), two of which are (S)-mephenytoin 4'hydroxylases (20, 21). P,-450 is the product of the CYP I Al gene (22) and is referred to as P-450 1A1 here. 5284 Downloaded from cancerres.aacrjournals.org on June 14, 2017. © 1991 American Association for Cancer Research. P-450 ACTIVATION OF CIGARETTE SMOKE tobacco and cigarette smoke condensate has made in vitro investigations difficult. In this work we utilized the so-called umu test for genotoxicity, where bacterial DNA damage induces the SOS response (27). Bioactivation of chemicals in an extract of cigarette smoke condensate, as measured by this assay, appears to be catalyzed primarily by P-450 1A2. The results are also consonant with a major role for arylamines in such extracts of cigarette smoke. MATERIALS AND METHODS Chemicals. AaC, PhIP, and 6-AC were gifts from Dr. F. F. Kadlubar, National Center for Toxicological Research (Jefferson, AR). Polycyclic hydrocarbon derivatives were obtained from the National Cancer Insti tute Repository through Midwest Research Institute (Kansas City, MO). Other procarcinogens and chemicals used were from the same sources described previously (28). Cigarette Smoke Condensate and Extraction of Carcinogens by Blue Cotton. Cigarette smoke condensate (standard 2R1 cigarette) was ob tained from the University of Kentucky Tobacco and Health Research Institute (Lexington, KY) and dissolved in (CH3)2SO or acetone at a concentration of 5 mg/ml. Extraction of carcinogens with blue cotton (copper phthalocyanine cellulose, Sigma Chemical Co., St. Louis, MO) was carried out with the methods described (29). Briefly, about 2 g of cigarette smoke condensate was dissolved in a small amount of (CH3)2SO and then diluted with H2O to 400 ml. To this solution was added about l g of blue cotton (which had been prewashed with (CH3)2SO, 2% concentrated NH4OH (v/v) in CH,,OH, and then exten sively with H2O). The extraction was carried out at room temperature with vigorous shaking for 1 h, and elution was done with 400 ml of 0.1% concentrated NH4OH in CH3OH (v/v) after extensive washing of the blue cotton with H2O. The overall recovery was about 3% (w/w), and the materials were dissolved in acetone to give a concentration of 5 mg/ml; this is referred to as "blue cotton extract." It was stored under argon at -70°C. Enzyme Preparations and Antibodies. Human liver samples were obtained from organ donors through Tennessee Donor Services and microsomal fractions were prepared as described elsewhere (30). Male rats (Sprague-Dawley strain, weighing about 250 g; HarÃ-anIndustries, Indianapolis, IN) were treated i.p. with each of several P-450 inducers: phénobarbital(80 mg/kg, daily for 3 days), BNF (50 mg/kg, daily for 3 days), ISF (100 mg/kg, daily for 3 days), PCN (80 mg/kg, daily for 3 days), or Aroclor (500 mg/kg, once). Rats were starved overnight before killing. Microsomes were prepared as described elsewhere (30). Human P-450Mp (31), P-450 3A4 (15), and P-450 1A2 (18) were prepared as described elsewhere. Rat P-450s 1A1, 1A2, and 2B1 (32) and rabbit P-450 l A2 (33) were purified to electrophoretic homogeneity as described previously. Rabbit anti-human P-450MP (31), anti-human P-450 3A4 (15), anti-rat P-450 1A1 (32), and anti-rat P-450 1A2 (32) preparations have been characterized previously. The anti-rat P-450 1Al antisera was cross-absorbed with microsomes prepared from livers of phenobarbital-treated rats (immobilized on gels) to remove antibod ies that react with P-450 1A2 (34). The anti-human P-450 3A4 prepa ration appears to recognize most or all of the human and rat P-450 3A enzymes (13, 14). IgG fractions were prepared and used to inhibit catalytic activities in microsomes (35). Rabbit liver NADPH-P-450 reducÃ-asewas purified by using the general procedure described by Yasukochi and Masters (36). Assays. Bufuralol 1'-hydroxylation (18, 37) and phenacetin O-deethylation (38) were determined as described elsewhere. Protein concen trations were estimated by using the Pierce bincinchonic acid procedure according to the manufacturer's directions (Pierce Chemical Co., Rockford, IL). P-450 was estimated spectrally from Fe2+-CO versus Fe2+ spectra as described by Omura and Sato (39). Protein immunoblotting was done as described elsewhere (34). Details of the umu gene expression assay for DNA damage are described elsewhere (27, 28, 40); in general, human and rat liver microsomes containing 10 to 100 pmol of P-450 were used with 0-25 Mgof cigarette smoke condensate or blue cotton extract (or 5 nmol of each procarcinogen when noted) in a volume of 1.0 ml of 50 mM potassium phosphate buffer (pH 7.4) containing a NADPH-generating system (consisting of 5 mM glucose-6-phosphate, 0.5 mM NADP+, and 1 IU yeast glucose-6-phosphate dehydrogenase/ml) and a suspension of bacterial tester strain Salmonella typhimurium TA1535/pSK1002 as described previously (27, 28, 40). In initial experiments we also used a new bacterial strain, S. typhimurium TA1535/pSK1002/pNM12, which overexpresses /V-acetyltransfer activity; the strain was kindly donated by Dr. Y. Oda, Osaka Prefectural Institute of Public Health (Osaka, Japan). Optimal conditions for the bioactivation of MelQ, IQ, 2-amino-6-methyldipyrido[l,2-a:3',2'-i/]imidazole, aflatoxin B,, and 6AC have already been reported in this laboratory (28) and were deter mined for the assays with A«Cand PhIP in the present study. In the reconstituted systems, microsomes were replaced with a premixed complex of (final concentrations in assay) 0.01-0.20 UM P-450, 0.05 MMrabbit NADPH-P-450 reducÃ-ase,and 7.5 nM L-a-dilauroyl-sn-glycero-3-phosphocholine. The expression of the umu gene was monitored by measuring fi-galactosidase activity (the product of a fused umuC'lacZ gene), and the bioactivation is presented as units of ßgalactosidase activity per min per mg protein or nmol P-450 (41). RESULTS Activation of Cigarette Smoke Condensate and Blue Cotton Extract by P-450 Enzymes. In order to optimize the reaction catalyzed by P-450 enzymes, we first examined the activation of cigarette smoke condensate by liver microsomes and recon stituted P-450 systems. The ability of the condensate to induce umu gene expression after metabolism by human and rat liver microsomes was very low (results not shown). However, when the reconstituted system containing human P-450 1A2 was used for the activation, considerable genotoxicity produced by crude cigarette smoke condensate was observed (Fig. 1). The genotoxic components of cigarette smoke condensate were ex tracted with blue cotton as described under "Materials and Methods" and were used in the umu assay in conjunction with P-450 enzymes. This extraction procedure has previously been shown to yield excellent recoveries of arylamines and other hydrophobic carcinogens (>60% from very crude and dilute solutions) (29,42-44). No response was observed in the absence of the enzymatic activation system. The genotoxic activity of the blue cotton extract was increased dramatically compared with that of the condensate, and the reaction was dependent on both the concentrations of P-450 1A2 and the condensate or extract (Fig. 1). However, when a high substrate concentration was included in the reaction mixture less activity was the result, probably reflecting the presence of inhibitors in the extract. Although the results are not presented here, it should be men- 0 100 200 Human P-4501A2 (pmol) Condensate or extract (ng/ml) Fig. 1. Dependence of umu gene response on amount of human P-450 IA2 (A) and on concentration of cigarette smoke condensate or blue cotton extract (B) in reconstituted monooxygenase systems. The basic incubation systems contained 0.05 nmol of P-450 and 5 »ig of either cigarette smoke condensate (•)or blue cotton extract (O) per ml. P-450 concentrations were varied as indicated in A. In B, the P-450 1A2 concentration was held constant and the amount of cigarette condensate or blue cotton extract was varied. 5285 Downloaded from cancerres.aacrjournals.org on June 14, 2017. © 1991 American Association for Cancer Research. P-450 ACTIVATION OF CIGARETTE SMOKE .5 150 o •¿ ~ 150 (AFB1) Effects of Cigarette Smoke Condensate or Blue Cotton Extract on Activation of Several Procarcinogens in Human Liver Micro somes. In order to examine the possibility that the cigarette smoke condensate contains some inhibitors of P-450 reactions as well as procarcinogens, we examined the effect of cigarette smoke condensate or blue cotton extract on the activation of several procarcinogens and bufuralol 1'-hydroxylation by liver (6-AC) 100 50 50 microsomes (Fig. 2). Cigarette smoke condensate caused a slight inhibition of the activation of aflatoxin B,, 6-AC, and 7,8-dihydroxy-7.8-dihydrobenzo(a)pyrene and bufuralol 1'-hy c o u u 12 Q. 150 C 24 12 24 150 (B(a)P-7,8-diol) o 100 50 o. O 12 24 Condensate o or extract 12 (ng ml) Fig. 2. Effects of cigarette smoke condensate (•)and blue cotton extract (O) on the activation of (.4) aflatoxin B, (AFB,); (B) 6-AC; (C) 7,8-dihydroxy-7.8dihydrobenzo(a)p>Tene [B(a)P-7,8-diol\\ and (D) bufuralol I '-hydroxylation cat alyzed by human liver microsomes (sample HL-I01). Control activities without the chemicals were 1201. 259, and 122 (umu) units/min/nmol P-450 for the bioactivation of aflatoxin BI, 6-AC, and 7.8-dihydroxy-7,8-dihydrobenzo(o)pyrene, respectively, and 0.33 nmol product formed/min/nmol P-450 for bufuralol 1'-hydroxylation. 100 24 (IQ) 100 12 24 Condensate 0 or extract 12 24 (ng/ml) Fig. 3. Effects of cigarette smoke condensate (•)and blue cotton extract (O) on the activation of (A) A«C.(A) PhlP. (C) MelQ. and (O) IQ catalyzed by human liver microsomes (sample HL-101). Control activities without the chem icals were 37, 67, 1301, and 826 units/min/nmol P-450 for the bioactivation of A«C,PhlP, MelQ, and IQ, respectively. droxylation; the former three reactions are known to be cata lyzed by P-450 3A4 and the latter hydroxylation by P-450 2D6 in human liver microsomes (18, 28, 45). Blue cotton extract, on the other hand, showed a much less inhibitory effect on these reactions. The effects of cigarette smoke condensate and blue cotton extract on the activation of A«C,PhlP, MelQ, and IQ catalyzed by human liver microsomes are shown in Fig. 3. The latter two reactions have been shown in this laboratory to be catalyzed mainly by P-450 1A2 in human liver, and the former two reactions are reported in this study to be catalyzed principally by the same enzyme (see below; see also Ref. 46). Cigarette smoke condensate showed potent inhibition of these activation reactions and blue cotton extract caused less but still consider able inhibition. On the basis of these results subsequent experiments were done by using 5 ^g of blue cotton extract per ml of incubation mixture; in this concentration range the inhibition of P-450 1A2 reactions was not so extensive and the activation of these components could readily be measured in the system. Activation of AaC, PhlP, and Blue Cotton Extract by Rat Liver Microsomes. The roles of P-450 enzymes in the activation of AivC, PhlP, and the blue cotton extract of cigarette smoke condensate were examined by using liver microsomes from variously pretreated rats (Table 1). The activation of A«Cand PhlP by liver microsomes could be enhanced by about 10-fold and 6-fold in rats treated with BNF and Aroclor, respectively, on the basis of units/min/nmol P-450. ISF was also an ¡mincer for the two reactions although not as potent as BNF. PCN also produced some increase in the activation of A«C(2-fold) and PhlP (4-fold). The trend for the activation of the blue cotton extract by rat liver microsomes seems to be similar to that of the activities of A«Cand PhlP activation, except that ISF was the strongest inducer in the case of the blue cotton extract and PCN did not cause an increase in the activation of the blue cotton extract. Activation of AaC, PhlP, and Blue Cotton Extract by Human Liver Microsomes. The genotoxic activities of A«C,PhlP, and the blue cotton extract were also determined in 9 human liver Table 1 Activation of AaC. PhlP, ana hlue cotton extract hy rat liver microsomes AnC (5 MM).PhlP (5 /IM). or blue cotton extract (5 tig/mi) was incubated with rat liver microsomes (0.05 MMP-450) in the presence of an NADPH-generating system and bacterial tester strain 5. typhimurium TA1535/pSK1002; the induced umu gene expression was determined as described in "Materials and Methods." Data presented are means of duplicate determinations with combined microsomal preparations from 3 rats ±SD (range). umu response (units/min/nmol P-450) cotton extract3.8 tioned that the use of a newly developed bacterial strain, S. typhimurium TA1535/pSK1002/pNM12, increased the genotoxic response seen by cigarette smoke condensate or the blue cotton extract but the enhanced response relative to the control was not overly dramatic. Control Phénobarbital BNF ISF PCN AroclorAaC2.3 2.3 23.3 10.4 5.4 13.0 ±1.2 12.4 ±0.6 ±3.7 64.1 ±1.4 37.1 ±1.6 29.7 40.5 ±2.0PhlP6.8 ±0.9 + 4.3 ±11.6 ±6.2 ±5.4 ±7.1Blue 5.4 8.1 11.6 4.0 14.0 ±2.9 ±2.2 ±3.2 + 2.9 ±1.9 ±4.1 5286 Downloaded from cancerres.aacrjournals.org on June 14, 2017. © 1991 American Association for Cancer Research. P-450 ACTIVATION OF CIGARETTE SMOKE Table 2 .Miration of AaC, PhIP, and hlue cotton extract hy human liver microsomes Experimental conditions are similar to those of Table 1, except that human liver microsomes from 9 individual samples were used. The results are presented as means of duplicate determinations. umu response (units/min/nmol P-450) (the activity was not as high when reconstituted in the presence of human cytochrome h*). Among the rat P-450 enzymes, P450s 1A1 and 1A2 catalyzed the activation of these compounds; rat P-450 2B1 was a poor catalyst. Rabbit P-450 1A2 could also catalyze the activation of AaC, PhIP, and the blue cotton extract. extract7.39.34.03.14.93.66.96.08.05.9 cotton SampleHL-99HL-101HL-102HL-105HL-107HL-110HL-112HL-113HL-124Mean Effects of Anti-P-450 IgG Preparations on Activation of AaC, PhIP, and Blue Cotton Extract Catalyzed by Rat and Human Liver Microsomes. The above results support the view that P450 1A enzymes may be the principal ones involved in the activation of these chemicals in liver microsomes. The effects of anti-P-450 IgG preparations on the microsomal activities in rats and humans were examined: anti-rat P-450 1A1 and antirat P-450 1A2 inhibited the activation of AaC catalyzed by ±2.1 ±SDAnC17.435.710.35.39.54.36.914.718.513.6 ±9.7PhIP37.860.721.76.011.88.523.919.737.325.3 ±17.5Blue liver microsomes from Aroclor-treated rats, and anti-human P450 1A2 caused about 50% inhibition of the human liver microsomal activation of AaC (Table 5). The effects of anti-PTable 3 Correlation of activities ofmonooxygena.se activities and amounts of microsomal components in human liver microsomal preparations 450 IgG preparations on the activation of PhIP catalyzed by Correlation coefficient (r) liver microsomes prepared from a human sample (HL-99) and Aroclor-treated rats are shown in Fig. 4. The activation of PhIP A«C PhIP Blue cotton extract was inhibited by anti-P-450 1A2 but not by anti-P-450 3A4 or 0.74 0.92 anti-P-450 2C IgG in human liver microsomes (Fig. 4/1). In 0.85 0.92 Blue cotton extract" 0.74 0.85 liver microsomes prepared from Aroclor-treated rats the en Glu P-1"'* 0.85 0.89 0.64 zymes catalyzing PhIP activation were inhibited by anti-rat PPhenacetin O-deethylation' 0.80 0.89 0.91 P-450 \\2d 0.81 0.90 0.78 450 1Al, anti-rat P-450 1A2, and anti-human P-450 3A4 IgG P-450Mp (2C)" 0.09 0.04 0.03 preparations (Fig. 4B). P-450 3A4* 0.43 0.05 0.03 Total P-450'' The effect of a human autoimmune antiserum on the activa 0.03 0.06 0.40 " Activation of procarcinogens (umu units/min/mg of protein). tion of the blue cotton extract by human liver microsomes is *Glu P-1. 2-amino-6-methyldipyrido(1.2-a:3'.2'-</)imidazole. shown in Fig. 5/1; these antibodies have been shown to selec ' Microsomal hydrox) lation (nmol product/min/mg of protein). tively recognize and inhibit human P-450 1A2 strongly (47). J P-450 content (nmol/mg of protein or blotting ¡mensity/mgof protein). The antiserum caused significant inhibition of activities of the blue cotton extract by liver microsomes. Anti-rat P-450 2D1 microsomal preparations (Table 2). The activities for A«Cand showed no effect on the activation of the blue cotton extract PhIP were found to be relatively high in human liver micro catalyzed by human liver microsomes (Fig. 5B); this particular somes as compared with rat liver microsomes. The mean activ antibody preparation had been shown to inhibit >90% of the ities (13.6 and 25.3 units/min/nmol P-450 for A«Cand PhIP, bufuralol 1'-hydroxylation in human liver microsomes when respectively) were greater than the activities obtained with the control rat preparations. The activation of the blue cotton Table 4 Activation of AaC, PhIP, and hlue cotton extract by reconstituted monooxygenase systems containing purified P-450 enzymes extract was also seen in human liver microsomal samples; the activities were always lower than those in A«Cand PhIP. In Experimental conditions were as in the legend to Table 1. except that recon order to identify the possible roles of P-450 enzymes in the stituted monooxygenase systems were used. Data are presented as means of duplicate or triplicate determinations. activation of these chemicals in human liver microsomes, we umu response (units/min/nmol P-450) determined several other parameters (catalytic activities and formsHuman P-450 amounts of individual P-450 enzymes) and made comparisons cotton extract34<1<1IS23418 P-4501A22C (Table 3). Good correlation could be seen between the rates of activation of A«C,PhIP, and 2-amino-6-methyldipyridol[l,2(P-450MP)3A4Rat a:3',2'-</]imidazole, phenacetin O-deethylation activity, and the P-4501A11A22B1Rabbit amount of P-450 1A2 in the 9 different human samples. The activation of the blue cotton extract was also correlated with the other activities and the amount of P-450 1A2. However, P-4501A2AaC741454034332PhIP125<144675171Blue other components, including the amounts of P-450\ip, P-450 3A4, or total P-450 showed poor correlation with the activation of A«C,PhIP, or the blue cotton extract. Reconstitution of Activation of AaC, PhIP, and Blue Cotton Table 5 Effects of anti-P-450 IgC preparations on the activation of AaC catalyzed hy liver microsomes of Aroclor-treated rats and a human sample Extract in Systems Containing Purified Forms of P-450. The Experimental conditions were described in "Materials and Methods." Data activation of AaC, PhIP, and the blue cotton extract were are presented as means of duplicate determinations ±SD (range). measured in reconstituted systems containing NADPH-P-450 geneexpression (units/min/nmol reducÃ-ase and several P-450 enzymes isolated from humans, P-450)Aroclor-treated rats, and rabbits (Table 4). Among the three human P-450 Anti-P-450None P-450III rats33.5 (HL-99)20.9 enzymes examined the rate measured with P-450 l A2 was the ± 8.2 ±2.8 highest for the activation of AaC, PhIP, and the blue cotton Preimmune 35.2 ±4.9 19.9 2.69.5 ± extract. The human P-450 2C enzyme (P-450MP) had consid Anti-rat P-450 1A1 10 8.4 ±1.9 Anti-rat P-450 1A2 102umu 16.1 ±4.2Human erable activity for AaC but not for PhIP or the blue cotton Anti-human P-450 1A2mg/nmol ±1.9 extract. P-450 3A4 showed some reactivity with AaC and PhIP 5287 Downloaded from cancerres.aacrjournals.org on June 14, 2017. © 1991 American Association for Cancer Research. P-450 ACTIVATION OF CIGARETTE SMOKE >. *« '> U a 100 •¿a a> 50 5 u I 0 5 10 Anti-P-450 o (mg 5 IgG/nmol 10 P-450) Fig. 4. Effects of anti-P-450 IgG preparations on the activation of PhIP catalyzed by liver microsomes from a human sample (HL-99) and from Aroclortreated rats. (A) Activation of PhIP by human liver microsomes in the presence of anti-P-450Mp (A). anti-P-450 3A4 (•).and anti-P-450 1A2 (O); (B) activation of PhIP by rat liver microsomes in the presence of anti-rat-P-450 1A1 (•),antirat-P-450 1A2 (O), anti-rat-P-450 2B1 (A), and anti-human P-450 3A4 (A) are shown. Control activities in the absence of the IgGs were 35 units/min/nmol P450 for human liver microsomes and 44 units/min/nmol P-450 for rat liver microsomes. S-, —¿150 150 - C o o *M (0 100' o 50 a. M 9 0> e 01 3 3 a E 0.0 0.5 1.0 Human serum (pi) 3 ) 5 10 Anti-P-450 2D1 (mg IgG/nmol P-450) Fig. 5. Effects of (A) human autoimmune antisera and (B) anti-P-450 2D1 IgG on the activation of blue cotton extract catalyzed by liver microsomes of a human sample, HL-IOI. In I. control sera (O) or autoimmune antisera (•)was included. Control activities without the serum or IgG were the same as in the legend to Fig. 5. used at the same concentration in parallel experiments (results not presented). Effects of 7,8-Benzoflavone and Quinidine on the Bioactivation of Blue Cotton Extract by Human Liver Microsomes. The effects of 7,8-benzoflavone and quinidine on the metabolic activation of the blue cotton extract catalyzed by liver microsomes were examined (Fig. 6). 7,8-Benzoflavone, a selective inhibitor of P450 1A2 (19), caused significant inhibition of the activities. Quinidine, a strong inhibitor of P-450 2D6 (48,49) was without effect on these reactions catalyzed by human liver microsomes. associated with low levels of bacterial mutagenesis (7, 52). Although some studies have suggested that bacterial mutage nesis is seen only in frameshift-dependent systems and is not dependent upon the SOS response (7), other studies have shown that base pair substitutions are also induced (8, 53) and that the mutagenicity is responsive to the SOS response (53). How ever, the level of mutagenicity is still relatively low in all of these systems. After considerable effort with S. typhimurium TA98 and the YG1006 and YG1024 strains containing overexpressed yV-acetyltransfer activity (54), we decided that the use of the induction of the umu response in an established test system was most appropriate. The use of such a system which overexpressed ¿V-acetyltransferasedid not dramatically enhance the response. A standard cigarette smoke condensate preparation was found to be highly inhibitory of the P-450-catalyzed oxidative activation of many promutagens (Fig. 3). This inhibition was particularly notable in the case of reactions catalyzed by P-450 l A2. The exact nature of this inhibition is unknown, and it is not clear that the inhibition is caused by the same chemicals which are genotoxic. A number of procedures have been re ported in the literature for the concentration of mutagens from tobacco-related mixtures and other crude carcinogens (8, 11, 51, 55). We found the so-called blue cotton extraction proce dure (29, 42-44) to be more efficient than polystyrene beads (8) or alumina chromatography (10, 56, 57). It is difficult to quantify the recovery of potentially mutagenic material because of the poor and variable response seen in the crude cigarette smoke condensate, but the apparent recovery was >100%, probably because of the removal of inhibitors. Consonant with previous reports, we found that the ability to activate cigarette smoke condensate (actually the blue cotton extract) was markedly less in human liver microsomes than in liver microsomes prepared from rats treated with P-450 inducers such as BNF, ISF, or Aroclor (Table 1) (7, 52). There was also some variation among individual human samples (Table 1), although not to the extent seen with some other P-450 reactions (24, 28). P-450 1A2 appears to be a major hepatic enzyme involved in the bioactivation of cigarette smoke con densate, or at least the blue cotton extract, as judged by (a) the inducibility of the response in rat liver (Table 1); (¿>) the corre lation seen between the response and several marker activities (Table 3); (c) inhibition of the activation by 7,8-benzoflavone and by antibodies raised against P-450 1A enzymes (Figs. 4 and DISCUSSION The purpose of these studies was to characterize the enzy matic activation of cigarette smoke condensate to genotoxic materials. This is difficult in light of the complexity of the material and the large number of carcinogens known to be present (9). One of the initial concerns was the choice of an assay system. While urine from cigarette smokers is known to be directly mutagenic to bacteria (8, 50, 51 ), the in vitro acti vation of cigarette smoke condensate itself to genotoxins is o 100 'co O) o o. X o o C 0) O) E 3 Inhibitor (uM) Fig. 6. Effects of 7,8-bcnzoflavone (•)and quinidine (O) on the bioactivation of blue cotton extract catalyzed by liver microsomes (sample of HL-IOI). The activity in the absence of added inhibitor was 11.2 units/min/nmol P-450. 5288 Downloaded from cancerres.aacrjournals.org on June 14, 2017. © 1991 American Association for Cancer Research. P-450 ACTIVATION OF CIGARETTE SMOKE 5); and (d) the demonstration of activity with P-450 1A2 enzymes isolated from rats, rabbits, and humans (Table 4). Cigarette smoking is known to induce human liver P-450 1A2 (58). It should be emphasized, however, that there is consider able evidence that P-450 1A2 is not expressed to a measureable degree in extrahepatic tissues (14). Indeed, McLemore et al. (59) did not detect P-450 1A2 in human lung samples, using an oligonucleotide probe and conditions of stringency that should have been appropriate (60) [the P-450 1A2 mRNA can be distinguished from the P-450 1A1 mRNA by its size (61)]. However, a wide variety of evidence indicates that P-450 1A1 is usually not expressed in human liver (14); the significance of tissue localization of P-450s is not totally clear in this regard, since mutagens may distribute from the liver after activation (62, 63). The matter of P-450 2D6 may be considered. Several inves tigations have linked the occurrence of the debrisoquine 4hydroxylation "poor metabolizer" phenotype with decreased risk of tobacco-associated lung cancer (2, 25, 64, 65). There have also been reports of similar associations with cancers in other tissues (66, 67), but there have been references to lack of association as well (68, 69). One hypothesis for the association has been that P-450 2D6 is catalyzing the bioactivation of a genotoxin in cigarette smoke to cause tumor initiation; indeed, certain epidemiológica! associations have been specifically cited to support such a view (2). However, with our in vitro screens we have been unable to find evidence to support such a view. For instance, the genotoxicity of the blue cotton extract was not inhibited by quinidine or anti-rat P-450 2D1 under condi tions known to extensively block bufuralol 1'-hydroxylation in human liver microsomes (Tables 2 and 3 and associated data). Qualitatively similar findings resulted from our assays involving mutations in 5. typhimurium TA98 (data not shown). It should also be emphasized that of all of the carcinogens examined in recent years, none has been found to be activated primarily by human P-450 2D6 (28, 70, 71). If there really is a relationship between P-450 2D6 and tumor initiation, then, what can it be due to? One possibility relates back to early studies on debri soquine 4-hydroxylation, when it was thought that the same enzyme was involved in phenacetin O-deethylation (72, 73). This view was subsequently disproven with the separation and purification of the two enzymes (18), and it is now finally clear that P-450 1A2 is the phenacetin 0-deethylase (13, 14, 19). Although the P-450 1A2 and 2D6 structural genes are on separate chromosomes (13), there is still in vitro and in vivo data suggesting some correlation in expression (18, 72). The basis of the relationship is speculatory, but it may be possible that the altered incidence of cancer may be related to P-450 1A2 and not to P-450 2D6 itself. In this regard, it would be of interest to know if the caffeine 3-demethylation phenotype (P450 1A2) (19) is associated with any of the cancers of interest. What is the major class of genotoxic material present in cigarette smoke condensate? This is not an easy question to answer in view of the many potentially tumorigenic materials in the mixture and the synergism and inhibition that might be expected (Figs. 2 and 3) (9, 10, 56, 57). Although polycyclic hydrocarbons and their dihydrodiol epoxides in particular have long been of concern in this regard, there is actually some evidence against them in the etiology of lung cancer induced by cigarette smoke, at least with regard to DNA adduct formation resulting from the stereoisomeric epoxides derived from 7,8dihydroxy-7,8-dihydrobenzo(a)pyrene. For instance, in the work of Randerath et al. (74), no "P-labeled DNA adducts corresponding to these and some related compounds were detected in smokers' lungs or placenta. Further, in rats treated with cigarette smoke condensate no such adducts were found under conditions where benzo(a)pyrene did yield the products (75). There is a considerable body of evidence to support the view that arylamines may be highly significant in smokinginduced cancer, at least at the level of tumor initiation. For instance, Kier et al. (7) reported the highest mutagenicity for a slightly basic fraction of cigarette smoke condensate, and other work has shown a correlation between the content of the arylamine A«C and the mutagenicity of different cigarette preparations (76). Peluso et al. (50) have presented evidence that a major fraction of the mutagenicity in smokers' urine is related to Phi P and its products. However, the significance of this conclusion must be considered in terms of the unusual stability of Ar-hydroxy-2-amino-l-methyl-6-phenylimidazo[4,5¿>]pyridine and the high activity of bacterial /V-acetyltransferases for some aryl hydroxylamines. Many arylamines have been detected in cigarette smoke condensate, some at high levels (11, 76, 77). Of these, A«Cseems to be present at the highest level (76) and, in our work, it had only somewhat less genotoxicity than PhIP (Table 1). Both rat P-450 1Al and P-450 1A2 can activate A«C(Table 4). While McManus et al. (46) have shown that recombinant human P-450 1A1 (primarily extrahepatic) is much inferior to human P-450 1A2 in activating IQ, MelQ, and MelQx, the activities toward PhIP are similar (46). This point may be of significance in consideration of the tissue distribution of these enzymes. However, the paradigm remains to be better clarified in light of the low concentrations of some of the arylamines that have exceptional genotoxicity in these assays (27, 28). Further, there is probably a considerable degree of variation among cigarette preparations (76, 78). Indeed, preliminary work indicates that Glu P-2, which has genotoxicity similar to A«Cor PhIP (28), is the main arylamine identified in the particular cigarette smoke condensate we have worked with.5 Another point is that the (rat) P-450 1Al enzymes have also been shown to detoxicate PhIP by C-hydroxylation (79). On the other hand, the slightly acidic fractions of cigarette smoke condensate have also been shown to possess tumor initiating and promoting properties (10, 57). Indeed, catechol has been identified as a cocarcinogen in this fraction (10). Nitrosamines cannot be ignored, for several are tobacco specific and present at levels as high as some of the arylamines in tobacco (9). The P-450s principally involved in the bioactivation of these remain to be elucidated. Further, the nitrosamines are notorious for not being detected readily in bacterial genotoxicity assays, as well as the umu test used here (28, 71), and the reason is probably not lack of the appropriate P-450s, for the P-450 2E1 substrates can be activated but still show a poor response (71). Thus, these might be overlooked in the in vitro work we have done here. Further, it is impossible to completely rule out a role for any enzyme (including P-450 2D6) in tumor initiation because the substrate may not produce an appropriate response in a particular set of assays. Finally, the caveat should be presented that tumor initiation may not be the only aspect of cancer related to cigarette smok ing. Epidemiological studies indicate that the cancer risk to individuals who stop smoking drops, even after many packyears of exposure. However, some of the undefined DNA ad ducts in exsmokers' lungs have been reported to persist for up to 14 years after smoking cessation (74), and the biologically relevant lesions are unknown. Further, the risk of urinary 5 F. F. Kadlubar. personal communication. 5289 Downloaded from cancerres.aacrjournals.org on June 14, 2017. © 1991 American Association for Cancer Research. P-450 ACTIVATION OF CIGARETTE SMOKE bladder cancer has been shown to be correlated with the inher ent mutagenicity of different types of tobacco (78). In summary, our work indicates that cigarette smoke conden sate is highly inhibitory of human P-450 catalytic activities, particularly those of P-450 1A2, and that in human liver microsomes much of the activation of components of the blue cotton extract to genotoxic materials can be attributed to P450 1A2 in liver microsomes of humans and experimental animals. The results are consonant with roles of arylamines such as AaC, PhIP, and 2-aminodipyrido[l,2-a:3',2'-rf]imidazole in mutagenicity associated with cigarette smoking. No positive evidence for a role of P-450 2D6 in the activation of genotoxins was obtained. Further studies will be required to establish the significance of these findings to tissue-specific cancers related to smoking. ACKNOWLEDGMENTS We thank Dr. D-H. Kim, T. Cheng, and A. Mower for carrying out preliminar)' studies. Dr. P. H. Beaune for the human anti-P-450 1A2 serum. Dr. M. Iwasaki for some of the reagents. Dr. Y. 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