Induction of sister-chromatid exchanges by indirect mutagens/carcinogens in cultured rat hepatoma and esophageal tumor cells and in Chinese hamster Don cells co-cultivated with rat cells

2 rat cell lines originated from ascites hepatoma AH66-B and esophageal tumor R1 were examined for their inducibility of sister-chromatid exchanges (SCEs) after treatment with 14 kinds of indirect mutagens/carcinogens, including 6 amine derivatives, 4 azo compounds, 3 aromatic hydrocarbons and 1 steroid. Of the 14 chemicals tested, 2-acetylaminofluorene (AAF), butylbutanolnitrosamine (BBN), dimethylnitrosamine (DMN), cyclophosphamide (CP), urethane, 2-methyl-4-dimethylaminoazobenzene (2-MeDAB), 3′-methyl-4-dimethylaminoazobenzene (3′-MeDAB), 4-o-tolylazo-o-toluidine (4-TT), benzo[a]pyrene (BP), 7,12-dimethyl-benz[a]anthracene (DMBA) and diethylstilbestrol (DES) were estimated to be effective inducers of SCEs in AH66-B and/or R1 cells, without the use of exogenous activating systems. Cell-mediated SCE tests with 6 selected chemicals, CP, 2-MeDAB, 4-TT, BP, DMBA and DES, showed a significant increase of SCEs in Chinese hamster Don-6 cells co-cultivated with AH66-B or R1 cells, depending on the number and sensitivity of AH66-B or R1 cells, as well as on the dose of chemicals tested, whereas singly cultured Don-6 cells were much less sensitive or almost insensitive to these chemicals. The above findings suggest that AH66-B and R1 cells may retain metabolic activities to convert a wide range of indirect mutagens/carcinogens into their active forms to induce SCEs, and that these cell lines provide simple and reliable screening systems in vitro, including the cell-mediated SCE assay, for detection of genotoxic agents, without the use of exogenous activation systems.     

Induction of in vivo DNA adducts by 4 industrial by-products in the rat-lung-cell system

Benz[a]anthracene (BA), dibenz[a,h]anthracene (DBA), dibenzo[a,i]pyrene (DBP), and dibenz[a,h]acridine (DBAC) are by-products found in many industrial wastes and emissions. Workers in the related occupational settings are potentially exposed to these substances through inhalation. In the present study, induction of DNA adducts in vivo by these chemicals was investigated using ³²P-postlabeling analysis in the rat-lung-cell system. The potency of DNA-adduct inducing activity was also compared to that of two cytogenetic endpoints i.e., sister-chromatid exchange (SCE) and micronucleus formation. Via intratracheal instillation, male CD rats (6/group) were dosed 3 times with BA, DBA, DBP or DBAC in a 24-h interval. Lung cells were enzymatically separated and used to determine the frequency of DNA adducts, SCE and micronuclei. Results show that all 4 test compounds induced DNA adducts, SCEs, and micronuclei in the rat-lung cell in vivo and that the postlabeling DNA adduct assay detected genotoxic activity at lower dose levels than the two cytogenetic assays. These findings suggest that BA, DBA, DBP or DBAC are rat pulmonary genetoxicants and the DNA-adduct assay is more sensitive than SCE or micronucleus assays for detecting the pulmonary genotoxicity of these industrial PAHs in the in vivo rat-lung-cell system.     

Induction of mutations by chemical agents at the hypoxanthine-guanine phosphoribosyl transferase locus in human epithelial teratoma cells

Induction of 6-thioguanine (TG) resistance by chemical mutagens was examined in a line of cells derived from a human epithelial teratocarcinoma cell clone. The cells, designated as P3 cells, have a stable diploid karyotype with 46(XX) chromosomes, including a translocation between chromosomes 15 and 20. Efficient recovery of TG-resistant mutants induced by the direct-acting mutagens: N-methyl-N′-nitro-N-nitrosoguanidine (MNNG); 7β,8α-dihydroxy-9α,10α-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BPDE); and benzo[a]pyrene (B[a]P); activated in a cell-mediated assay, required an expression time of 7 days and a saturation density of 2 × 10⁴ cells/60-mm petri dish. The TG-resistant mutant cells induced by MNNG and BPDE maintained their resistant phenotype 4–6 weeks after isolation. This mutant phenotype was associated with a more than 10-fold reduction in hypoxanthine-guanine phosphoribosyl transferase (HGPRT) activity relative to that of the parental P3 cell line, which was shown to catalyze the formation of 4.6 pmoles inosine-5′-monophosphate (IMP)/min/μg protein. Induction of TG resistance was also observed in P3 cells cocultivated in a cell-mediated assay with human breast carcinoma cells, which are capable of polyclinic aromatic hydrocarbon (PAH) metabolism, after treatment with the carcinogenic PAHs: B[a]P, chrysene, 7,12-dimethylbenz[a]anthracene (DMBA), and 3-methylcholanthrene (MCA). The degree of mutant induction in this assay was related to the carcinogenic potency of these PAHs in experimental animals. The most potent mutagen was DMBA, followed in decreasing order by MCA, B[a]P, and chrysene. DMBA, at 0.4 μM, increased the frequency of mutants for TG resistance from 2 for the control to about 200 TG-resistant mutants/10⁶ colony-forming cells (CFC). Benzo[e]pyrene (B[e]P) and pyrene, which are not carcinogenic, were not effective in the assay. None of the PAHs was mutagenic in the P3 cells cultivated in the absence of the PAH-metabolizing cells. These results indicate that the P3 cells can be useful for the study of mutagenesis at the HGPRT locus by direct-acting chemical mutagens, as well as by chemicals activated in a cell-mediated assay.     

The metabolism of 7- and 12-methylbenz[a]-anthracene and their derivatives

1. 7- and 12-Methylbenz[a]anthracene were converted by rat-liver homogenates into the corresponding hydroxymethyl derivatives, products that are probably the 8,9-dihydro-8,9-dihydroxy and the 5,6-dihydro-5,6-dihydroxy derivatives, and a number of phenolic products. 2. Both hydrocarbons were converted into glutathione conjugates; that from 7-methylbenz[a]anthracene was also formed, together with 5,6-dihydro-5,6-dihydroxy- and 5-hydroxy-benz[a]anthracene, from 5,6-epoxy-5,6-dihydro-7-methylbenz[a]anthracene. 3. 7- and 12-Hydroxymethyl-benz[a]anthracene were converted into products that are probably 8,9-dihydro-8,9-dihydroxy derivatives, and into phenols. 4. The preparation of a number of derivatives of the hydrocarbons is described. 5. The oxidation of the hydrocarbons with lead tetra-acetate was investigated.     

Differences in responses of 4 adult rat-liver epithelial cell lines to a spectrum of chemical mutagens

An assay for mutagenesis at the hypoxanthine-guanine phosphoribosyl transferase (HGPRT) locus in adult rat-liver epithelial cell cultures (ARL) has been developed to take advantage of the capacity of this cell type to metabolically activate promutagens/procarcinogens. A survey of the effect of 5 types of activation-dependent mutagens/carcinogens on 4 ARL lines indicates that the ARL/HGPRT mutagenesis assay with the 4 target cell lines is able to detect a spectrum of activation-dependent carcinogens. Individual ARL lines, however, responded quite differently to a given carcinogen. The ARL/HGPRT mutagenesis assay system thus offers distinct possibilities for the study of the control of chemical biotransformation processes. However, in light of the specificity of the various cell lines to respond to a particular class of mutagens under the current assay condition, this particular assay system cannot be readily applied to routine screening of suspected environmental mutagens of unknown requirements for metabolic activation. Nevertheless, for agents with a structure related to those activated by a specific line, this system can be used to study mutagenesis resulting from intact cellular metabolism.     

Chromosomal aberration tests on 29 chemicals combined with S9 mix in vitro

A metabolic activation system with rat-liver microsome fraction plus cofactors (S9 mix) was applied to chromosomal aberration tests in vitro for the screening of chemical mutagens or carcinogens in the environment.Dialkylnitrosamines only induced chromosomal aberrations in Chinese hamsters cells (CHL) when treated with S9 mix. The incidence of chromosomal aberrations in CHL varied with experimental conditions, e.g. incubation time, recovery time, components of S9 mix and inducers used for preparation of S9, For dimethylnitrosamine (DMN), the maximal incidence was obtained when the cells were incubated with S9 mix for 3 h and harvested 24 h after treatment. Therefore, this system (3 h incubation and 24 h recovery) was routinely applied to further screening of other chemicals with S9 prepared from PCB-pretreated rats. 10 carcinogens (e.g. 7, 12-dimethylbenz [a] anthracene, benzo-[a] pyrene, quinoline, etc.) out of 16 induced aberrations when they were treated with S9 mix, whereas the remaining 6 carcinogens (e.g., 3-methylcholanthrene, 4-o-tolylazo-o-toluidine, etc.) induced few or no aberrations even after activation. Two insecticides, allethrin and diazinon, were strongly positive at relatively low doses only when they were activated with the S9 mix. Medical drugs, such as ethenzamide, methyl p-hydroxybenzoate and nitrofurazone, and a food additive, sodium hypchlorite, were positive on activation. Chemicals used for industry, such as styrene monomer and tris-dichloropropylphosphate, were also positive in our activation system.     

The metabolism of a series of polycyclic hydrocarbons by mouse skin maintained in short-term organ culture

Investigations on the metabolism of ³H-labelled chrysene, benz[a]anthracene, 7-methylbenz[a]anthracene, 7,12-dimethylbenz[a]anthracene, 3-methylcholanthrene, benzo[a]pyrene, dibenz[a,c]anthracene and dibenz[a,h]anthracene by mouse skin maintained in short-term organ culture were carried out. Estimations of the distribution of the metabolites of each hydrocarbon present after 24 h showed that there were wide variations both in the rates at which the hydrocarbons were metabolised and in the amounts of metabolites covalently bound to skin macromolecules. All the hydrocarbons were metabolised to dihydrodiols, which were identified by comparison on high pressure liquid chromatography (HPLC) with the authentic compounds, and these were the same diols as those that were formed in previous experiments with rat-liver microsomal fractions. However, free dihydrodiols represented only relatively small proportions of the total amounts of metabolites formed. All the hydrocarbons yielded dihydrodiols of the type that could give rise to bay-region diol-epoxides, when further metabolised, some of which are thought to be involved in hydrocarbon carcinogenesis.     

Promutagen activation by rodent-liver postmitochondrial fractions in the L5178Y/TK cell mutation assay

Individual S9 microsomal fractions prepared from normal livers of 8 rodent species or strains and from 1 rat strain pretreated with Aroclor 1254, were used to metabolize the promutagens N-acetyl-2-aminofluorene, 1,2--benzanthracene, to metabolize the promutagens N-acetyl-2-aminofluorene, 1,2-benzanthracene, benzo[a]pyrene, and 3-methylcholanthrene to active forms during 3-h co-incubation in the presence of L5178Y/TK^+/− cells. The 8 compatible S9 preparations all converted each of the 4 chemical carcinogens into active mutagens with varied efficiencies except for the Aroclor-induced rat S9/benzanthracene combination which produced only weak activity. Aroclor induction did not notably enhance the mutagenicity of benzo[a]pyrene or 3-methylcholanthrene beyond that activity mediated by the other non-induced preparations. Syrian hamster S9 and, to a lesser degree, C57BL/6J mouse S9 were exceptionally active in converting N-acetyl-2-aminofluorene to toxic and mutagenic metabolites. One source of Swiss mouse liver (Blu : Ha ICR) provided the most active S9 when tested with the 3 polycyclic aromatic hydrocarbons.In general, mutagenicity and cytotoxicity were roughly correlated within S9 + promutagen combinations. Almost all of the methylcholanthrene metabolizing activity was lost by the 12th week when Aroclor-induced rat S9 was held at −20°C, yet this activity remained constant when similar S9 was stored at −80°C for 14 weeks. Surprisingly, some S9 sources including the induced rat-liver preparation converted anthracene to a weak or border-line mutagen. The activation of both 1,2-benzanthracene and anthracene may be linked within each species or strain although Aroclor induction enhanced anthracene mutagenicity yet attenuated the mutagenicity of 1,2-benzanthracene. Collectively, these data underscore the current inchoate state of development for S9 coupled somatic cell mutation assays.     

Sister-chromatid exchange induction by indirect mutagens/carcinogens, aryl hydrocarbon hydroxylase activity and benzo[alpha]pyrene metabolism in cultured human hepatoma cells

2 human hepatoma cell lines (C-HC-4 and C-HC-20), in which aryl hydrocarbon hydroxylase activity was induced with benz[alpha]anthracene in vitro to about 140- and 64-fold of the respective basal levels, yielded an increased frequency of sister-chromatid exchanges (SCEs) when exposed to benzo[alpha]pyrene (BP), 7,12-dimethylbenz[alpha]anthracene and 3-methylcholanthrene in vitro. Analysis of the metabolism of BP by these cells by high-pressure liquid chromatography revealed that both cell lines produced various BP metabolites including the proximate form BP-7,8-dihydrodiol which has been reported to be the most potent inducer of SCEs among the metabolites of BP. In addition, aflatoxin B1 and cyclophosphamide also induced SCEs in these cell lines. The above findings suggest that these cells may be capable of metabolizing a range of indirect mutagens/carcinogens into DNA-active forms. These cells may therefore serve as a useful test system in vitro for the detection of genotoxic agents, without the use of an exogenous activating system.     

Differential excision of carcinogenic hydrocarbon-DNA adducts in mouse embryo cell cultures.

Primary mouse embryo cell cultures efficiently excise DNA damage introduced by the carcinogens 7-bromomethylbenz[$\text{a}$]anthracene and 3-methylcholanthrene but are inefficient in excision of damage introduced by 7,12-dimethylbenz[a]anthracene. Since exposure of the cells to the latter compound does not impair their capacity for excision of adducts introduced by the bromocompound, it is concluded the 7,12-dimethylbenz[$\text{a}$]anthracene-DNA adducts are intrinsically difficult to excise.     

Epoxy derivatives of aromatic polycyclic hydrocarbons. The preparation of benz[a]anthracene 8,9-oxide and 10,11-dihydrobenz[a]anthracene 8,9-oxide and their metabolism by rat liver preparations

The syntheses of 10,11-dihydrobenz[a]anthracene 8,9-oxide, benz[a]anthracene 8,9-oxide and 9-hydroxybenz[a]anthracene are described, together with those of a number of related compounds. The epoxides react both chemically and enzymically with water to yield the corresponding dihydrodiols and with reduced glutathione to form glutathione conjugates, and they react chemically with N-acetylcysteine to yield the corresponding mercapturic acids. 8,9-Dihydro-8,9-dihydroxybenz[a]anthracene, formed enzymically from benz[a]anthracene 8,9-oxide, was identical with a dihydrodiol formed when benz[a]anthracene was metabolized by rat liver homogenates. Similarly 10,11-dihydrobenz[a]anthracene 8,9-oxide yielded a dihydrodiol identical with the product formed when 10,11-dihydrobenz[a]anthracene was metabolized.     

Announcement

Aryl hydrocarbon hydroxylase (AHH) was present in explant cultures of human prostate obtained from surgery of benign prostatic hyperplasia and was inducible by benz[a]anthracene (BA). The induction of AHH ranged from 14- to 150-fold when compared with control values and 10-fold variation of AHH inducibility among individuals was observed. Epithelial cells grown from human prostate tissue also contained measurable AHH activity and AHH was inducible by BA and 7,12-dimethylbenz[a]anthracene (DMBA). Inducibility of AHH by BA ranged from 2- to 63-fold. The inducibility of AHH by DMBA was always less than that by BA. In cells treated with N-methyl-N′-nitro-N-nitrosoguanidine (MNNG), there were no changes in AHH activity. These findings support the view that the human prostate is susceptible to environmental polycyclic hydrocarbon carcinogens and that environmental and occupational factors might contribute to the etiology of human prostatic carcinoma.     

Combined Genotoxic Effects of a Polycyclic Aromatic Hydrocarbon (B(a)P) and an Heterocyclic Amine (PhIP) in Relation to Colorectal Carcinogenesis

Colorectal neoplasia is the third most common cancer worldwide. Environmental factors such as diet are known to be involved in the etiology of this cancer. Several epidemiological studies have suggested that specific neo-formed mutagenic compounds related to meat consumption are an underlying factor involved in the association between diet and colorectal cancer. Heterocyclic amines (HCAs) and polycyclic aromatic hydrocarbons (PAHs) are known mutagens and possible human carcinogens formed at the same time in meat during cooking processes. We studied the genotoxicity of the model PAH benzo(a)pyrene (B(a)P) and HCA 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP), alone or in mixture, using the mouse intestinal cell line Apc^Min/+, mimicking the early step of colorectal carcinogenesis, and control Apc^+/+ cells. The genotoxicity of B(a)P and PhIP was investigated using both cell lines, through the quantification of B(a)P and PhIP derived DNA adducts, as well as the use of a genotoxic assay based on histone H2AX phosphorylation quantification. Our results demonstrate that heterozygous Apc mutated cells are more effective to metabolize B(a)P. We also established in different experiments that PhIP and B(a)P were more genotoxic on Apc^Min/+ cells compared to Apc^+/+. Moreover when tested in mixture, we observed a combined genotoxicity of B(a)P and PhIP on the two cell lines, with an increase of PhIP derived DNA adducts in the presence of B(a)P. Because of their genotoxic effects observed on heterozygous Apc mutated cells and their possible combined genotoxic effects, both B(a)P and PhIP, taken together, could be implicated in the observed association between meat consumption and colorectal cancer.     

Benz[a]anthracene Biotransformation and Production of Ring Fission Products by Sphingobium sp. Strain KK22

A soil bacterium, designated strain KK22, was isolated from a phenanthrene enrichment culture of a bacterial consortium that grew on diesel fuel, and it was found to biotransform the persistent environmental pollutant and high-molecular-weight polycyclic aromatic hydrocarbon (PAH) benz[a]anthracene. Nearly complete sequencing of the 16S rRNA gene of strain KK22 and phylogenetic analysis revealed that this organism is a new member of the genus Sphingobium. An 8-day time course study that consisted of whole-culture extractions followed by high-performance liquid chromatography (HPLC) analyses with fluorescence detection showed that 80 to 90% biodegradation of 2.5 mg liter⁻¹ benz[a]anthracene had occurred. Biodegradation assays where benz[a]anthracene was supplied in crystalline form (100 mg liter⁻¹) confirmed biodegradation and showed that strain KK22 cells precultured on glucose were equally capable of benz[a]anthracene biotransformation when precultured on glucose plus phenanthrene. Analyses of organic extracts from benz[a]anthracene biodegradation by liquid chromatography negative electrospray ionization tandem mass spectrometry [LC/ESI(−)-MS/MS] revealed 10 products, including two o-hydroxypolyaromatic acids and two hydroxy-naphthoic acids. 1-Hydroxy-2- and 2-hydroxy-3-naphthoic acids were unambiguously identified, and this indicated that oxidation of the benz[a]anthracene molecule occurred via both the linear kata and angular kata ends of the molecule. Other two- and single-aromatic-ring metabolites were also documented, including 3-(2-carboxyvinyl)naphthalene-2-carboxylic acid and salicylic acid, and the proposed pathways for benz[a]anthracene biotransformation by a bacterium were extended.     

Unexpected DNA damage caused by polycyclic aromatic hydrocarbons under standard laboratory conditions

The genotoxicity of 15 polycyclic aromatic hydrocarbons was determined with the alkaline version of the comet assay employing V79 lung fibroblasts of the Chinese hamster as target cells. These cells lack the enzymes necessary to convert PAHs to DNA-binding metabolites. Surprisingly, 11 PAHs, i.e., benzo[a]pyrene (BaP), benz[a]anthracene, 7,12-dimethylbenz[a]anthracene, 3-methylcholanthrene, fluoranthene, anthanthrene, 11H-benzo[b]fluorene, dibenz[a,h]anthracene, pyrene, benzo[ghi]perylene and benzo[e]pyrene caused DNA strand breaks even without external metabolic activation, while naphthalene, anthracene, phenanthrene and naphthacene were inactive. When the comet assay was performed in the dark or when yellow fluorescent lamps were used for illumination the DNA-damaging effect of the 11 PAHs disappeared. White fluorescent lamps exhibit emission maxima at 334.1, 365.0, 404.7, and 435.8 nm representing spectral lines of mercury. In the case of yellow fluorescent lamps these emissions were absent. Obviously, under standard laboratory illumination many PAHs are photo-activated, resulting in DNA-damaging species. This feature of PAHs should be taken into account when these compounds are employed for the initiation of skin cancer.The genotoxicity of BaP that is metabolically activated in V79 cells stably expressing human cytochrome P450-dependent monooxygenase (CYP1A1) as well as human epoxide hydrolase (V79-hCYP1A1-mEH) could not be detected with the comet assay performed under yellow light. Likewise the DNA-damaging effect of r-7,t-8-dihydroxy-t-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BaPDE) observed with the comet assay was only weak. However, upon inhibition of nucleotide excision repair (NER), which is responsible for the removal of stable DNA adducts caused by anti-BaPDE, the tail moment rose 3.4-fold in the case of BaP and 12.9-fold in the case of anti-BaPDE. These results indicate that the genotoxicity of BaP and probably of other compounds producing stable DNA adducts are reliably detected with the comet assay only when NER is inhibited.     

An in vitro chromosome assay using cultured rat-liver cells

An in vitro chromosome assay has been developed which utilises an epithelial-like cell line derived from rat liver. The cell line, designed RL₁, retains sufficient metabolic enzyme activity to detect chromosome damage induced by a variety of chemical mutagens and carcinogens without the incorporation of an extrinsic metabolising system. The cells are grown on standard glass microscope slides, exposed to the test chemical and processed in situ for metaphase analysis.In a small validation study, chromosome damage was detected in cultures exposed to the direct-acting agents, methyl nitronitrosoguanine, 4-nitroquinolineN-oxide, propylene oxide, epichlorohydrin and 1,2 : 3,4-diepoxybutane and to compounds requiring metabolic activation, including cyclophosphamide, 2-acetylaminofluorene, 3-methylcholanthrene and 7,12-dimethylbenz[α]anthracene. Negative results were obtained with pyrene and carbon tetrachloride.     

Oncogene alterations in in vitro transformed rat tracheal epithelial cells

10 derivations of rat tracheal epithelial (RTE) cells, including normal cells, normal primary cultures, 7 tumorigenic cell lines and 1 nontumorigenic cell line transformed in vitro by treatment with 7,12-dimethyl-benz[a]anthracene (DMBA), benzo[a]pyrene (BP) and/or 12-O-tetradecanoylphorbol-13-acetate (TPA) were examined for oncogene alterations. No abnormalities of Ha-ras were seen that were suggestive of amplification, rearrangement or the presence of RFLPs. Analysis of specific-point mutations in Ha-ras using Pst I digestion (codon 12, GGA to GCA) or Ha-ras and Ki-ras using Xba I (codon 61, CAA to CTA) were negative. In one cell line derived by DMBA treatment, changes in the c-myc restriction digest pattern were seen after incubation with Bam HI and Hind III. Northern analysis revealed consistent differences between normal and transformed cells when probed with Ha-ras; c-myc expression was of low intensity, and the expression of Ki-ras could not be detected. Transfection of RTE cell DNAs into NIH/3T3 cells did not result in the appearance of morphologic transformants. The studies suggest that Ha-ras or Ki-ras codon 61 A to T transversions (CAA to CTA) are not associated with the immoral/tumorigenic phenotype in RTE cells transformed by DMBA or TPA, and are in contrast to results reported in some other biological systems.     

Mutagenic and chemical assay of extracts of airborne particulates

The mutagenic activity of extracts of airborne particulates was evaluated in the Salmonella system. The mutagenicity of airborne particulates was not always correlated with the content of benzo[a]pyrene (B[a]P) in the complex mixtures, especially when the samples were collected at different sites.Large-scale fractionation of extracts of airborne particulates was used to determine the content of specific mutagenic chemicals. The neutral fraction of material soluble in cyclohexane and nitromethane contained the polycyclic aromatic hydrocarbon (PAH) compounds, which accounted for 27.9% of the mutagenic activity of the whole extracts. 9 kinds of PAH compound were identified quantitatively by thin-layer chromatography. They included, per 1000 m³ of air, 12.6 μg of benzo[e]pyrene (B[e]P), 10.7 μg of chrysene (CHRY), 10.0 μg of fluoranthene (FL), 6.43 μg of benzo[ghi]perylene (B[ghi]P), 5.75 μg of benz[a]anthracene (B[a]A), 5.33 μg of B[a]P, 3.38 μg of pyrene (PYR), 1.83 μg of coronene (COR), and 1.34 μg of perylene (PERY).Mutagenicity of the ether-soluble acidic, basic and methanol-soluble neutral fractions accounted for 10.9, 9.71 and 6.78% of the total mutagenic activity of crude extract, respectively, when assayed in strain TA98 with liver S9 fraction. The total recovery of mutagenic activity after fractionation was 58%.Two acidic fractions (weak and strong ether-soluble acids) and the methanol-soluble neutral fraction reverted strain TA98 dramatically to prototrophy in the presence of rat-lung S9 fraction more than liver. But the mutagenic chemicals in these fractions remain to be clarified. Direct mutagens were present in essentially all fractions.The particulates, which had diameters ranging from 0.3 to 1.0 μm and were able to penetrate alveoli, contained a high content of mutagens.     

Metabolism of polycyclic compounds. The metabolism of 7,12-dimethylbenz[a]anthracene by rat-liver homogenates

1. The main products of the metabolism of 7,12-dimethylbenz[a]anthracene by rat-liver homogenates are the isomeric monohydroxymethyl derivatives. The syntheses of these compounds are described. 2. Two phenolic products and two dihydrodihydroxy compounds were formed, but none of these appeared to have been formed by hydroxylation at the `K region''. There was little evidence for the formation of a glutathione conjugate of the hydrocarbon. 3. The monohydroxymethyl derivatives are products of the hydroxylation of the hydrocarbon in the ascorbic acid–Fe²⁺–oxygen model hydroxylating system.     

Benzo-[a]-pyrene induces FAK activation and cell migration in MDA-MB-231 breast cancer cells

Benzo-[a]-pyrene (B[a]P) is a family member of polycyclic aromatic hydrocarbons and a widespread environmental pollutant. It is a mammary carcinogen in rodents and contributes to the development of human breast cancer. However, the signal transduction pathways induced by B[a]P and its role in breast cancer progression have not been studied in detail. Here, we demonstrate that B[a]P induces cell migration through a lipoxygenase- and Src-dependent pathway, as well as the activation of focal adhesion kinase, Src, and the extracellular signal-regulated kinase 2 in MDA-MB-231 breast cancer cells. However, B[a]P is not able to promote migration in the mammary nontumorigenic epithelial cells MCF12A. Moreover, B[a]P promotes an increase of αvβ3 integrin–cell surface levels and an increase of metalloproteinase (MMP)-2 and MMP-9 secretions. In summary, our findings demonstrate that B[a]P induces the activation of signal transduction pathways and biological processes involved in the invasion/metastasis process in MDA-MB-231 breast cancer cells.