Transformation of normal hamster cells by benzo(a)pyrene diol-epoxide

Malignant transformation of human colon epithelial cells by benzo[c]phenanthrene dihydrodiolepoxides as well as 2-hydroxyamino-1-methyl-6-phenylimidazo[4,5-b]pyridine

Polycyclic aromatic hydrocarbons (PAHs) and heterocyclic aromatic amines (HCAs) ingested with food have repeatedly been suggested to be involved in the malignant transformation of colon epithelial cells. In order to test this hypothesis, HCEC cells (SV40 large T antigen-immortalized human colon epithelial cells) were incubated with a racemic mixture of benzo[c]phenanthrene dihydrodiol epoxides (B[c]PhDE), extremely potent carcinogenic PAH metabolites in vivo, or with 2-hydroxyamino-1-methyl-6-phenylimidazo[4,5-b]pyridine (N-OH-PhIP), the N-hydroxylated metabolite of the most abundant HCA in cooked meat. First, it was shown that HCEC cells express sulfotransferase 1A1, which is needed to metabolize N-OH-PhIP to the corresponding N-sulfonyloxy derivative, the direct precursor molecule of genotoxic nitrenium ions. Thereafter, exponentially growing HCEC cells were exposed five times to 0.1 microg (0.37 nmol) B[c]PhDE/ml for 30 min or 0.72 microg (3 nmol) N-OH-PhIP/ml for 24 h. Chemically treated HCEC cells showed an enhanced saturation density and grew faster than the corresponding solvent-treated cell cultures. After five treatment cycles, HCEC(B[c]PhDE) as well as HCEC(N-OH-PhIP) cells lost cell-cell contact inhibition and started piling up and forming foci in the culture flasks. Furthermore, HCEC(B[c]PhDE) and HCEC(N-OH-PhIP) cells were injected i.m. into SCID mice. Within 6 weeks after injection, eight animals out of eight injected with HCEC(B[c]PhDE) or HCEC(N-OH-PhIP) cells developed tumors at the site of injection, thus demonstrating the high tumorigenic potential of the HCEC(B[c]PhDE) and HCEC(N-OH-PhIP) cell cultures. Taken together, we show for the first time that the abovementioned active PAH metabolites as well as N-OH-PhIP are indeed able to malignantly transform human colon epithelial cells in vitro.

Comparison of the genotoxic activities of the K-region dihydrodiol of benzo[a]pyrene with benzo[a]pyrene in mammalian cells: morphological cell transformation; DNA damage; and stable covalent DNA adducts

Benzo[a]pyrene (B[a]P) is the most thoroughly studied polycyclic aromatic hydrocarbon (PAH). Many mechanisms have been suggested to explain its carcinogenic activity, yet many questions still remain. K-region dihydrodiols of PAHs are metabolic intermediates depending on the specific cytochrome P450 and had been thought to be detoxification products. However, K-region dihydrodiols of several PAHs have recently been shown to morphologically transform mouse embryo C3H10T1/2CL8 cells (C3H10T1/2 cells). Because K-region dihydrodiols are not metabolically formed from PAHs by C3H10T1/2 cells, these cells provide a useful tool to independently study the mechanisms of action of PAHs and their K-region dihydrodiols. Here, we compare the morphological cell transforming, DNA damaging, and DNA adducting activities of the K-region dihydrodiol of B[a]P, trans-B[a]P-4,5-diol with B[a]P. Both trans-B[a]P-4,5-diol and B[a]P morphologically transformed C3H10T1/2 cells by producing both Types II and III transformed foci. The morphological cell transforming and cytotoxicity dose response curves for trans-B[a]P-4,5-diol and B[a]P were indistinguishable. Since morphological cell transformation is strongly associated with mutation and/or larger scale DNA damage in C3H10T1/2 cells, the identification of DNA damage induced in these cells by trans-B[a]P-4,5-diol was sought. Both trans-B[a]P-4,5-diol and B[a]P exhibited significant DNA damaging activity without significant concurrent cytotoxicity using the comet assay, but with different dose responses and comet tail distributions. DNA adduct patterns from C3H10T1/2 cells were examined after trans-B[a]P-4,5-diol or B[a]P treatment using 32P-postlabeling techniques and improved TLC elution systems designed to separate polar DNA adducts. While B[a]P treatment produced one major DNA adduct identified as anti-trans-B[a]P-7,8-diol-9,10-epoxide-deoxyguanosine, no stable covalent DNA adducts were detected in the DNA of trans-B[a]P-4,5-diol-treated cells. In summary, this study provides evidence for the DNA damaging and morphological cell transforming activities of the K-region dihydrodiol of B[a]P, in the absence of covalent stable DNA adducts. While trans-B[a]P-4,5-diol and B[a]P both induce morphological cell transformation, their activities as DNA damaging agents differ, both qualitatively and quantitatively. In concert with the morphological cell transformation activities of other K-region dihydrodiols of PAHs, these data suggest a new mechanism/pathway for the morphological cell transforming activities of B[a]P and its metabolites.

Synergistic mechanisms in carcinogenesis by polycyclic aromatic hydrocarbons and by tobacco smoke: a bio-historical perspective with updates

B[a]P (benzo[a]pyrene) has been used as a prototype carcinogenic PAH since its isolation from coal tar in the 1930's. One of its diol epoxides, BPDE-2, is considered its ultimate carcinogen on the basis of its binding to DNA, mutagenicity and extreme pulmonary carcinogenicity in newborn mice. However, BPDE-1 has a similar binding to DNA and mutagenicity but it is not carcinogenic. In addition, BPDE-2 is a weak carcinogen relative to B[a]P when repeatedly applied to mouse skin, the conventional assay site. Its carcinogenicity is increased when applied once as an initiator followed repeatedly by a promoter. This indicates a major role for promotion in carcinogenesis by PAHs. Promotion itself is a 2-stage process, the second of which is selective propagation of the initiated cells. Persistent hyperplasia underlies selection by promoters. The non-carcinogenicity of BPDE-1 has yet to be resolved. PAHs have long been considered the main carcinogens of cigarette smoke but their concentration in the condensate is far too low to account by themselves for the production of skin tumors. The phenolic fraction does however have strong promotional activity when repeatedly applied to initiated mouse skin. Several constituents of cigarette smoke are co-carcinogenic when applied simultaneously with repeated applications of PAHs. Catechol is co-carcinogenic at concentrations found in the condensate. Since cigarette smoking involves protracted exposure to all the smoke constituents, co-carcinogenesis simulates its effects. Both procedures, however, indicate a major role for selection in carcinogenesis by cigarette smoke. That selection may operate on endogenous mutations as well as those induced by PAHs. There are indications that the nicotine-derived NNK which is a specific pulmonary carcinogen in animals contributes to smoking-induced lung cancer in man. Lung adenoma development by inhalation has been induced in mice by the gas phase of cigarette smoke. The role of selection has not been evaluated in either of these cases.

Biotransformation of trans-4,5-dihydroxy-4,5-dihydrobenzo[a]pyrene to benzo[a]pyrene bis-diols and DNA adducts by induced rat liver microsomes

The biotransformation of (+/-)-trans-4,5-dihydroxy-4, 5-dihydrobenzo[a]pyrene (trans-B[a]P-4,5-diol), the K-region dihydrodiol of B[a]P, by beta-naphthoflavone (BNF)-induced rat liver microsomes was studied. trans-B[a]P-4,5-diol was metabolized to six major products as characterized by NMR, MS, and UV spectroscopy, and all were identified as bis-diols: two diastereomers of trans,trans-4, 5:7,8-tetrahydroxy-4,5:7,8-tetrahydrobenzo[a]pyrene (trans, trans-B[a]P-4,5:7,8-bis-diol), two diastereomers of trans,trans-4, 5:9,10-tetrahydroxy-4,5:9,10-tetrahydrobenzo[a]pyrene (trans, trans-B[a]P-4,5:9,10-bis-diol), and two diastereomers of the somewhat unusual trans,trans-1,2:4,5-tetrahydroxy-1,2:4, 5-tetrahydrobenzo[a]pyrene (trans,trans-B[a]P-1,2:4,5-bis-diol). BNF-induced rat liver microsomes also metabolized B[a]P to the same trans-B[a]P-4,5-diol-derived bis-diols. The ability of trans-B[a]P-4, 5-diol to form DNA adducts was investigated using (32)P-postlabeling techniques specifically designed to detect stable polar DNA adducts. Four DNA adducts were detected after microsomal activation of trans-B[a]P-4,5-diol with calf thymus DNA. Further analyses indicated that each of these stable polar DNA adducts was derived from the further metabolic activation of the trans,trans-B[a]P-4,5:7, 8-bis-diols. We conclude that trans-B[a]P-4,5-diol can be metabolized to a series of B[a]P-bis-diols, and can also be metabolically activated to form stable polar DNA adducts. The trans, trans-B[a]P-4,5:7,8-bis-diols were shown to be metabolic intermediates in the formation of these DNA adducts.

ATSDR evaluation of health effects of chemicals. IV. Polycyclic aromatic hydrocarbons (PAHs): understanding a complex problem

Polycyclic Aromatic Hydrocarbons (PAHs) are a group of chemicals that are formed during the incomplete burning of coal, oil, gas, wood, garbage, or other organic substances, such as tobacco and charbroiled meat. There are more than 100 PAHs. PAHs generally occur as complex mixtures (for example, as part of products such as soot), not as single compounds. PAHs are found throughout the environment in the air, water, and soil. As part of its mandate, the Agency for Toxic Substances and Disease Registry (ATSDR) prepares toxicological profiles on hazardous chemicals, including PAHs (ATSDR, 1995), found at facilities on the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) National Priorities List (NPL) and which pose the most significant potential threat to human health, as determined by ATSDR and the Environmental Protection Agency (EPA). These profiles include information on health effects of chemicals from different routes and durations of exposure, their potential for exposure, regulations and advisories, and the adequacy of the existing database. Assessing the health effects of PAHs is a major challenge because environmental exposures to these chemicals are usually to complex mixtures of PAHs with other chemicals. The biological consequences of human exposure to mixtures of PAHs depend on the toxicity, carcinogenic and noncarcinogenic, of the individual components of the mixture, the types of interactions among them, and confounding factors that are not thoroughly understood. Also identified are components of exposure and health effects research needed on PAHs that will allow estimation of realistic human health risks posed by exposures to PAHs. The exposure assessment component of research should focus on (1) development of reliable analytical methods for the determination of bioavailable PAHs following ingestion, (2) estimation of bioavailable PAHs from environmental media, particularly the determination of particle-bound PAHs, (3) data on ambient levels of PAHs metabolites in tissues/fluids of control populations, and (4) the need for a critical evaluation of current levels of PAHs found in environmental media including data from hazardous waste sites. The health effects component should focus on obtaining information on (1) the health effects of mixtures of PAHs particularly their noncarcinogenic effects in humans, and (2) their toxicokinetics. This report provides excerpts from the toxicological profile of PAHs (ATSDR, 1995) that contains more detailed information.

Comparison of the standard and reduced pH Syrian hamster embryo (SHE) cell in vitro transformation assays in predicting the carcinogenic potential of chemicals

A comprehensive review of the Syrian Hamster Embryo (SHE) cell transformation literature was performed in order to catalogue the chemical/physical entities which have been evaluated for in vitro cell transformation potential. Both reduced pH (pH 6.7) and standard pH (pH 7.1-7.3) SHE cell testing protocols were considered. Based upon this analysis, over 472 individual chemical/physical agents and 182 combinations of chemical/physical agents have been tested under the standard pH conditions, while over 56 chemical/physical agents have been tested under reduced pH conditions. Of the 472 chemical/physical agents tested at the standard pH, 213 had in vivo carcinogenicity data available. Of these 213 chemical/physical agents, 177 were carcinogens while 36 were non-carcinogens. The results of testing the SHE transformability of these 213 chemical/physical agents indicates that the standard pH SHE cell transformation assay had a concordance of 80% (171/213), a sensitivity of 82% (146/177), and a specificity of 69% (25/36). Of these 213 chemical/physical agents, 53% (112/213) were tested more than once often in more than one laboratory, with a 82% (92/112) interlaboratory agreement rate, thus providing confirmatory results. Carcinogenicity data were available for 48 of the 56 chemical/physical agents tested for SHE cell transformation under the reduced pH conditions. The SHE cell transformation assay under reduced pH conditions had a concordance of 85% (41/48), a sensitivity of 87% (26/30), and a specificity of 83% (15/18). For Salmonella-negative carcinogens, the standard pH SHE assay correctly predicted carcinogenicity 75% (48/64) of the time while the reduced pH SHE assay correctly predicted carcinogenicity for Salmonella-negative carcinogens 78% (14/18) of the time. For chemical/physical agents tested under both the reduced pH and standard pH conditions, the standard pH and reduced pH SHE cell assays had a 69% (22/32) agreement rate. Under the reduced pH conditions, the SHE assay correctly predicted rodent carcinogenicity in 86% (25/29) of the chemicals tested under both reduced and standard pH conditions. Under standard pH conditions, the SHE assay correctly predicted rodent carcinogenicity in 69% (20/29) of the chemicals tested under both reduced and standard pH conditions. Collectively, these data indicate that the SHE cell transformation assay is predictive for rodent carcinogenicity under either reduced or standard pH conditions. Importantly, the assay displays better performance and appears to have improved carcinogen prediction capability under reduced pH conditions.

Effect of duration of exposure to benzo(a)pyrene diol-epoxide on neoplastic transformation, mutagenesis, cytotoxicity, and total covalent binding to DNA of rodent cells

We examined the effect of different durations of exposure (20 sec to 24 hr) to (+/-) 7-beta,8 alpha-dihydroxy-9 alpha, 10 alpha -epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene (BPDE I) on the induction of transformation in C3H/10T 1/2 cells and of mutations to 6-thioguanine resistance in Chinese hamster ovary cells (CHO), as well as on BPDE I-DNA binding in these two cell lines. A 20-sec exposure of the cells to BPDE I was sufficient to induce mutations and morphological transformation in vitro. However, the transformation frequency in CH3 mouse-embryo-derived 10T 1/2 cells increased twofold and the frequency of mutations in CHO cells sixfold when the exposure time to BPDE I was increased from 20 sec to 8 h. Cytotoxicity increased under similar conditions. A large number of BPDE I-DNA adducts were formed in both cell lines within the first 15-min of exposure of the cells to this ultimate carcinogen. The total covalent binding did not increase with longer than 15-min incubation times. These results suggest that in addition to its covalent binding to DNA, BPDE I may influence other cellular mechanism(s) that are responsible for the initiation of transformation and mutagenesis.

Morphological transforming activity and metabolism of cyclopenta-fused isomers of benz[a]anthracene in mammalian cells

4 isomeric cyclopenta-derivatives of benz[e]anthracene (benz[a]aceanthrylene, benz[j]aceanthrylene, benz[l]aceanthrylene, and benz[k]acephenanthrylene) were examined for their ability to morphologically transform C3H10T1/2CL8 mouse-embryo fibroblasts. All of these polycyclic aromatic hydrocarbons studied except benz[k]acephenanthrylene transformed C3H10T1/2CL8 cells to both type II and type III foci in a concentration-dependent fashion. Benz[j]aceanthrylene was the most active, equivalent in activity to benzo[a]pyrene on a molar basis, in producing dishes of cells with transformed foci (94% at 1.0 microgram/ml). Benz[e]aceanthrylene, and benz[l]aceanthrylene produced 58% and 85% of the dishes with foci respectively at 10 micrograms/ml. Metabolism studies with [3H]benz[j]aceanthrylene in C3H10T1/2CL8 cells in which unconjugated, glucuronic acid conjugated, and sulfate conjugated metabolites were measured indicated that the dihydrodiol precursor to the bay-region diol-epoxide, 9,10-dihydroxy-9,10-dihydrobenz[j]aceanthrylene, was the major dihydrodiol formed (55%). Smaller quantities of the cyclopenta-ring dihydrodiol, 1,2-dihydroxy-1,2-dihydrobenz[j]aceanthrylene (14%), and the k-region dihydrodiol, 11,12-dihydroxy-11,12-dihydrobenz[j]aceanthrylene (5%) were also formed. Similar studies with [14C]benz[l]aceanthrylene indicated that the k-region dihydrodiol, 7,8-dihydroxy-7,8-dihydrobenz[l]aceanthrylene was the major metabolite formed (45%). The cyclopenta-ring dihydrodiol, 1,2-dihydroxy-1,2-dihydrobenz[l]aceanthrylene and 4,5-dihydroxy-4,5-dihydrobenz[l]aceanthrylene were formed in minor amounts (less than 6%). Therefore, metabolism at the cyclopenta-ring of B(j)A and B(l)A is a minor pathway in C3H10T1/2CL8 cells in contrast to previously reported studies with cyclopenta[cd]pyrene in which the cyclopenta-ring dihydrodiol was the major metabolite. These results suggest that routes of metabolic activation other than oxidation at the cyclopenta-ring such as bay region or k-region activation may play an important role with these unique polycyclic aromatic hydrocarbons in C3H10T1/2CL8 cells.

Benzo[a]pyrene metabolites: effects on viral interferon induction

Benzo[a]pyrene (BaP) metabolites were assessed, with and without enzymatic activation by rat liver S9, for their inhibitory activities on influenza virus induction of interferon-alpha/beta (IFN-alpha/beta) in mammalian (LLC-MK2) cell cultures. Although BaP per se was inactive, metabolized BaP reduced viral IFN induction by approximately 80%. BaP metabolites (phenols, diols, 6-substituted derivatives) exhibited significant inhibitory activity (50% or greater) only when they were activated enzymatically. Although not significant, the diol metabolites without activation mildly reduced IFN induction on the average of 32%. The quinones did not adversely affect the IFN induction process, but three of the seven metabolites tested showed approximately 30% inhibitory activity in the presence of S9. BaP diol epoxides were direct inhibitors of viral IFN induction while derivatives of these epoxides, tetrols and triols, showed negligible inhibition even with S9. In general, the reported microbial mutagenicities of BaP metabolites could be correlated with their abilities to inhibit IFN induction. That activation-dependent hydrocarbons can be metabolized by S9 added to mammalian cell cultures resulting in the inhibition of viral IFN induction extends the capability and credibility for assessing suspect mutacarcinogens on this basis.

Interactions of molecules with nucleic acids. X. Covalent intercalative binding of the carcinogenic BPDE I(+) to kinked DNA

A theoretical model is proposed for the covalent binding of (+) 7 beta,8 alpha-dihydroxy-9 alpha,10 alpha-epoxy-7,8,9,10- tetrahydrobenzo[a]pyrene denoted by BPDE I(+), to N2 on guanine. The DNA must kink a minimum of 39 degrees to allow proper hybrid configurations about the C10 and N2 atoms involved in bond formation and to allow stacking of the pyrene moiety with the non-bonded adjacent base pair. Conservative (same sugar puckers and glycosidic angles as in B-DNA) and non-conservative (alternating sugar puckers as in intercalation sites) conformations are found and they are proposed structures in pathways connecting B-DNA, an intercalation site, and a kink site in the formation of a covalently intercalative bound adduct of BPDE I(+) to N2 on guanine. Stereographic projections are presented for (3') and (5') binding in the DNA. Experimental data for bending of DNA by BPDE, orientation of BPDE in DNA and unwinding of superhelical DNA is explained. The structure of a covalent intercalative complex is predicted to result from the reaction. Also, an anti----syn transition of guanine results in a structure which allows the DNA to resume its overall B-form. The only change is that guanine has been rotated by 200 degrees about its glycosidic bond so that the BPDE I(+) is bound in the major groove. The latter step may allow the DNA to be stored with an adduct which may produce an error in the genetic code.

Association of benzo[a]pyrene with H1 histone in rat-liver nuclei

Rat-liver nuclei were incubated with microsomal fraction, NADPH and [3H]benzo[a]pyrene ([3H]BP). From the incubated nuclei, H1 histone was extracted and purified. The purified histone was acid-hydrolyzed; the hydrolysate was filtered on a column of Sephadex LH-20. The 4 radioactive fractions thus obtained by methanol gradient were about 44% of the total radioactivity. By thin-layer chromatography, 1 ninhydrin-positive and fluorescent spot was detected in each of the 2 radioactive fractions. The gas chromatographic and mass spectrometric analyses suggest that 1 of these 2 fractions contains a BP-diol epoxide-lysine conjugate.

Cell transformation by chemical agents--a review and analysis of the literature. A report of the U.S. Environmental Protection Agency Gene-Tox Program

The literature on cell transformation by chemical carcinogens has been critically reviewed. This subject is highly relevant to carcinogenesis in vivo, because the phenotypic changes that are collectively referred to as cell transformation usually involve the acquisition of tumorigenicity on inoculation into suitable rodent hosts. The systems chosen for review fall into 3 categories: cell strains (cells with a limited lifespan); cell lines (cells with an unlimited lifespan); and oncogenic viral-chemical interactions involving cells (Fischer rat embryo cells expressing an endogenous retrovirus, mouse embryo cells expressing the AKR leukemia virus, chemical enhancement of a simian adenovirus, SA7 transformation of Syrian hamster or rat embryo cells). Of the entire literature reviewed, 117 papers have been accepted for data abstraction by pre-defined criteria; these include 41 references to cell strains, 40 in cell lines, and 38 in viral-chemical interactions including cells. Because different systems have been reviewed, it would be meaningless to group all the compounds. The overall summary of the systems is as follows (many compounds have been tested in more than one system and, hence, are duplicated in these totals). (Chart: see text) In general, there is a reasonably good correlation between the results of the cell transformation systems and in vivo carcinogenesis. However, the many deficiencies of the EPA Merged Carcinogen List preclude definitive comparisons. Moreover, a number of 'false negatives' were obtained in systems that did not employ external metabolic activation. Further validation of all systems is required, but it seems very probable that several cell transformation systems will become valuable in assaying (with reasonable time and cost) the carcinogenic potential of environmental chemicals.

Metabolism of benzo[a]pyrene by fish cells in culture

Benzo[a]pyrene (BaP) metabolism was studied in cell lines derived from rainbow trout (RTG-2), bluegill fry (BF-2), and fathead minnow (FHM). Confluent cultures were exposed to 3H-BaP (0.5 nmol/ml), and, after various exposure times, metabolites were extracted from the media with an organic solvent and analyzed by high-pressure liquid chromatography. BF-2 and RTG-2 cells converted 63% of the BaP to water-soluble metabolites within 24 h, while FHM cells converted only 12%. BF-2 and RTG-2 cells metabolized more than 90% of the BaP by 48 h, while only 67% of the BaP was converted to water-soluble metabolites by FHM cells after 96 h. The major organic-solvent-extractable metabolites in all three cell lines were 9,10-dihydroxy-9,10-dihydrobenzo[a]pyrene and unidentified polar metabolites. Of the water-soluble metabolites formed by BF-2, FHM, and RTG-2 cells, 67, 42, and 19%, respectively, were converted to ethyl-acetate-extractable metabolites by treatment with beta-glucuronidase. All three cell lines formed a glucuronide of 7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (7,8-diol); in BF-2 and FHM cells, the 7,8-diol represented almost half of the metabolites released by beta-glucuronidase treatment. Thus, cell lines derived from three widely distributed species of freshwater fish have the capacity to metabolize BaP to a form that is a proximate carcinogen in rodents and to produce a water-soluble conjugate of this metabolite.

Benzo[a]pyrene 4,5-oxide. Discrepancy between induction of sister chromatid exchange and binding to DNA in cultured human fibroblasts

Benzo[a]pyrene 4,5-oxide was covalently bound to DNA of cultured human fibroblasts and caused sister chromatid exchange. The monooxygenase inhibitor alpha-napthoflavone suppressed this induction of sister chromatic exchange, but did not affect binding to DNA. Control experiments with 4-nitroquinoline 1-oxide showed that alpha-naphthoflavone does not inhibit sister chromatid exchange in general. A more likely explanation for the discrepancy between induction of sister chromatid exchange and binding to DNA is that benzo[a]pyrene 4,5-oxide itself can bind to DNA, but this binding does not lead to a significant increase in sister chromatid exchange. However benzo[a]pyrene 4,5-oxide can be oxidized by monooxygenase to yet unknown products which are potent inducers of sister chromatid exchange. An important conclusion from this is that a biological effect such as the induction of sister chromatid exchange may correlate with the exact nature of DNA binding rather than with total binding, to the point where just measuring total binding may be completely misleading if intended to detect the causes of the biological effect.

Mechanism of benzo[a]pyrene diol epoxide induced deoxyribonucleic acid strand scission

Approximately 1% of (+/-)-7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BaP-diol epoxide) DNA alkylation sites rearrange with strand scission at neutral pH. Phosphotriester hydrolysis and depurination/depyrimidination strand scission were critically examined as possible mechanisms for this phenomenon. The catalysis of nicking by alkali and the inhibition of nicking by counterions were consistent with either mechanism. The kinetics of nicking, however, were characteristic of a multistep reaction such as depurination/depyrimidination strand scission and the detection of apurinic sites in BaP-diol epoxide alkylated DNA strongly supported this mechanism. The number of such sites, especially at lower reaction levels, was probably sufficient to account for strand scission. No direct evidence was obtained for nicking occurring through phosphotriester hydrolysis. Studies with model substrates, including dibutyl phosphate, DNA homopolymers, and TMV RNA, indicated that if BaP-diol epoxide forms phosphotriesters in DNA or RNA, they do not hydrolyze with strand scission. Besides apurinic/apyrimidinic sites, a second alkali-sensitive rearrangement product was present in BaP-diol epoxide modified DNA. These latter sites accumulated with time and after 24 h accounted for as much as 4% of the initial alkylation events. Although relatively stable at neutrality, they spontaneously nicked the DNA backbone at high pH. It is possible that these sites represent a rearrangement of the major N2 guanine adduct.

Mutagenic activity of vinyl compounds and derived epoxides

Many vinyl compounds, such as vinyl chloride and some inhalational anesthetics, are known to be mutagens. In the present study, 10 vinyl compounds or derived epoxides, widely used in industry, were assayed in the Salmonella typhimurium/mammalian microsome system. 3 strains of histidine-dependent S. typhimurium, TA1535, TA98 and TA100 were used. Of the 10 compounds, 4 were mutagens. They were 9-vinylanthracene, vinylcarbazole, 3-vinyl-7-oxabicyclo[4.1.0]heptane and 3-epoxyethyl-7-oxabicyclo[4.1.0]-heptane. The study confirmed the overall genotoxicity of vinyl compounds and epoxides and the need to carefully screen them for mutagenic/carcinogenic effects.

Modification of deoxyribonucleic acid by a diol epoxide of benzo[a]pyrene. Relation to deoxyribonucleic acid structure and conformation and effects on transfectional activity

The effects of secondary structure on DNA modification by (+/-)-7 beta, 9 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10-tetrahydrobenzol[a]pyrene [(+/-)BPDE I] were investigated. No differences in the total extent of (+/-) BPDE I binding to double- and single-stranded calf thymus DNA were found. High-performance liquid chromatography (LC) of the nucleoside adducts obtained from hydrolysates of native and denatured calf thymus, as well as from superhelical and linear plasmid DNA, indicated that in all cases the major adduct (60--80% of total adducts) was formed by reaction of the (+) enantiomer of BPDE I with the N-2 position of dG residues in the DNA. A minor adduct formed from the reaction of the (-) enantiomer with dG residues was also detected and was present in greater amounts in denautred DNA than in native DNA. Small amounts of BPDE I--dA and BPDE I--dC adducts were also detected in both the single- and double-stranded DNAs. Restriction enzyme analysis of BPDE I modified SV40 and phage lambda DNA provided evidence that the modification of DNA by this carcinogen is fairly random with respect to nucleotide sequence. Partial hydrolysis of modified plasmid DNA by the single-strand-specific S1 nuclease and LC analysis of the nucleoside adducts in the digested and undigested fractions of the DNA revealed no preferential excision by the S1 nuclease of the different BPDE I--deoxynucleoside adducts. Functional changes in BPDE I modified DNA were demonstrated. With increasing extents of modification, there was a decrease in the ability of plasmid DNA to transfect a receptive Escherichia coli strain to antibiotic resistance.

Mutagenicity to mammalian cells in culture by (+) and (-) trans-7,8-dihydroxy-7,8-dihydrobenzo(a)pyrenes and the hydrolysis and reduction products of two stereoisomeric benzo(a)pyrene 7,8-diol-9,10-epoxides

The mutagenicity for mammalian cells of benzo(a)pyrene (BP) and 9 of its derivatives was tested by resistance to ouabain in Chinese hamster V78 cells. The derivatives included the (-) and (+) enantiomers of trans-7,8-diol; the racemic (+/-)trans-7,8-diol; two triols, (7/8,9)-triol and (7,9/8)-triol; and four tetrols, (7,10/8,9)-tetrol, (7/8,9,10)-tetrol, (7,9/8,10-triol and (7,9,10/8)-tetrol. Since V78 cells do not metabolize polycyclic hydrocarbons, mutagenesis was tested both in the presence and in the absence of Golden hamster cells capable of metabolizing polycyclic hydrocarbons. Neither BP nor any of its 9 tested derivatives showed mutagenicity for V78 cells in the absence of normal Golden hamster cells. However, in the presence of these cells, BP and the optically active and racemic trans-7,8-diols exhibited a mutagenic response that was dose-dependent. All other derivatives were inactive. The most active mutagenic hydrocarbon was (-) trans-7,8-diol, and activity decreased in the order (+/-)trans-7,8-diol, (+) trans-7,8-diol and BP.