Bacterial mutagenicity of new cyclopenta-fused cata-annelated polycyclic aromatic hydrocarbons, and identification of the major metabolites of benz[j]acephenanthrylene formed by Aroclor-treated rat liver microsomes

Three novel cyclopenta-fused polycyclic aromatic hydrocarbons were synthesized, benz[d]aceanthrylene, benz[k]aceanthrylene, and benz[j]acephenanthrylene, and evaluated for mutagenic activity in the Ames Salmonella typhimurium plate incorporation assay. The two benzaceanthrylene derivatives were active at low S9 concentrations in strain TA98 (4 and 27 rev/nmole respectively), as had been predicted from the calculated delta Edeloc/beta values of the carbocations derived from opening of the cyclopenta-fused epoxide rings, but the majority of this mutagenicity appeared to be due to free-radical decomposition products of spontaneous endo-peroxide formation. These compounds were therefore not further investigated. Benz[j]acephenanthrylene was also an indirect-acting frameshift mutagen (8-12 rev/nmole in strain TA98), but unlike most of the previously assayed cyclopenta-fused polycyclic aromatic hydrocarbons exhibited no peak of activity at low S9 protein concentration. The principal metabolites formed from this compound by microsomes from Aroclor-treated rat liver were benz[j]acephenanthrylene-4,5-dihydro-4,5-diol (necessarily derived from hydration of benz[j]acephenanthrylene 4,5-oxide) and benz[j]acephenanthrylene-9,10-dihydro-9,10-diol (precursor to benz[j]acephenanthrylene-9,10-dihydrodiol 7,8-oxide, the bay-region diol-epoxide). Consideration of the reduced activity of this compound compared to the related structure chrysene, the S9 dependence curves, and the predicted delta Edeloc/beta values of the postulate active species, suggests that in contrast to most other cyclopenta-fused polycyclic aromatic hydrocarbons, bay-region diol-epoxide formation plays a greater role than epoxidation of the cyclopenta-fused ring in the metabolic activation of benz[j]acephenanthrylene.     

High mutagenicity and toxicity of a diol epoxide derived from benzo[a]pyrene

(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BP 7,8-diol-9,10-epoxide) is a suspected metabolite of benzo[a]pyrene that is highly mutagenic and toxic in several strains of $\text{Salmonella}\text{typhimurium}$ and in cultured Chinese hamster V79 cells. BP 7,8-diol-9,10-epoxide was approximately 5, 10 and 40 times more mutagenic than benzo[a]pyrene 4,5-oxide (BP 4,5-oxide) in strains TA 98 and TA 100 of $\text{S.}\text{typhimurium}$ and in V79 cells, respectively. Both compounds were equally mutagenic to strain TA 1538 and non-mutagenic to strain TA 1535 of $\text{S.}\text{typhimurium}$. The diol epoxide was toxic to the four bacterial strains at 0.5–2.0 nmole/plate, whereas BP 4,5-oxide was nontoxic at these concentrations. In V79 cells, the diol epoxide was about 60-fold more cytotoxic than BP 4,5-oxide.     

Mutagenic activity of nitro-substituted cyclopenta-fused polycyclic aromatic hydrocarbons towards Salmonella typhimurium

Cyclopenta-fused isomers of pyrene and benz[a]anthracene, nitrated on the etheno bridge, were synthesized and tested in the Ames plate-incorporation assay. Since enzymatic reduction, if it occurs in these compounds, would form arylhydroxylamines which in turn would form highly stabilized arylnitrenium ions, we hoped to test the hypothesis that the direct-acting mutagenic activity of nitroPAH is correlated with the degree of stabilization of the electrophilic intermediate. We found that these compounds are mutagenic (1-9 rev/nmole in Salmonella typhimurium TA98) and do not require S9 activation. However, this activity is substantially lower than that of other nitroPAH of comparable size such as 1-nitropyrene (250-300 rev/nmole). The reasons for this comparative lack of activity are discussed with reference to current theories regarding structure-activity relationships of nitroPAH.     

Microbial mutagenicity of 3- and 4-ring polycyclic aromatic sulfur heterocycles

The stable isomers of 3- and 4-ring polycyclic aromatic sulfur heterocycles were tested for mutagenicity in the Ames standard plate incorporation test and a liquid pre-incubation modification of the Ames test. Of the 4 three-ring compounds tested, only naphtho[1,2-b]thiophene was mutagenic. Of the four-ring compounds, 7 of 13 were mutagenic in the standard Ames or pre-incubation Ames test. The highest activity for the 4-ring compounds was observed for phenanthrol[3,4-b]thiophene, a compound of approximately the same mutagenic potency in the Ames test as benzo[a]pyrene. The other active 4-ring compounds were of considerable less mutagenic potency than phenanthrol[3,4-b]thiophene. Mutagenicity for two of the 4-ring aromatic thiophenes could only be detected in the liquid pre-incubation Ames test. Salmonella typhimurium TA100 was the most sensitive strain to mutagenesis by these compounds, followed by TA98. All mutagenesis was indirect, requiring metabolic activation.     

Mutagenicity of wood smoke condensates in the Salmonella/microsome assay

Smoke condensates of woods used for food preservation and aromatization in Nigeria were tested for mutagenic activity using Salmonella typhimurium TA98 and TA100. The woods were: white mangrove (Avicennia nitida), red mangrove (Rhizophora racemosa), mahogany Khaya sp.), abura (Mitragyna ciliata), alstonia (Alstonia boonei) and black afara (Terminalia ivorensis). Cigarette tar was tested for comparison. The condensates induced dose-dependent increases in the number of His+ revertants mainly with S9 mix. With the exception of mahogany and cigarette smoke condensate, the smoke condensates induced more revertants/microgram condensate in TA100 than in TA98. The number of revertants/microgram condensate ranged between 0.04 and 0.9 for the wood smoke condensates and was 0.12 for the cigarette smoke in TA100. The range was between 0.1 and 0.30 for the wood smoke condensates and 0.18 revertants/microgram condensate for cigarette smoke condensate in TA98. Concentrations of 7 polycyclic aromatic hydrocarbons (PAHs) in the condensates were determined namely, pyrene, benzo[a]pyrene, benz[a]anthracene, benzo[k]fluoranthene, benzo[b]chrysene, benzo[g,h,i]perylene and dibenzo[a,e]pyrene. The condensates contained varying concentrations of the individual PAHs and those with higher concentrations generally showed greater mutagenic activities. However, the order of mutagenic potency in the bacterial strains differed from the order of PAH concentrations, which were lower than the concentrations at which they are reported to induce mutations. When 6 of the PAHs were mixed in the concentrations in which they were found in the individual condensates, the mixtures did not induce mutation so that the contribution of the PAHs to the mutagenic activities of the condensates could not be determined.     

Use of recombinant DNA techniques in cloning DNA repair genes and in the study of metagenesis in mammalian cells

18 polycyclic aromatic hydrocarbons (PAHs) and 7 quinones were tested for mutagenicity using Salmonella typhimurium TA97, TA98 and TA100 with or without metabolic activation. In the presence of metabolic activation, TA97 was more susceptible to mutation than either TA98 or TA100 by many of PAHs tested. PAHs such as 1-methylphenanthrene, fluoranthene, pyrene, benzo[a]pyrene, benzo[e]pyrene and perylene had high mutagenic effects on TA97 in the presence of metabolic activation. 1,6- and 1,8-pyrenequinones were also highly mutagenic on TA97 in the presence or absence of metabolic activation. It appears that pyrene is mutagenic through its metabolic conversion to pyrenequinones.     

Synthesis and structure--mutagenicity relationship of benzo-annulated cyclopentaphenanthrenes.

The synthesis of 2,3-dihydro-1H-indeno[5,4-a]anthracene (2), the fluoreno[a]anthracenes 3 and 4, 2,3-dihydro-1H-cyclopenta[a]chrysene (6), 3,4-dihydro-2-vinylphenanthrene (10) and cyclopenta[c]chrysenes 11, 12 has been described. Structure analysis of the new products by (1)H and (13)C NMR spectroscopy is presented. Estimates of the mutagenic activity of compounds 2--4, 6 and 11--14 in Salmonella typhimurium determined by Ames' test indicate that all products are inactive for both TA 98 and TA 100 strains except 4,5-dihydro-3H-cyclopenta[c]chrysene (12). The mutagenic properties of these compounds have been compared with those shown by previously studied benzo[g]cyclopenta[a]phenanthrenes and cyclopenta[c]phenanthrenes and discussed. Some conclusions have been drawn about the effects of benzoannulation and of the carbonyl function on the mutagenicity of this class of compounds.     

Mutagenicity of C24H14 PAH in human cells expressing CYP1A1

Relatively little is known about the mutagenicity of C24H14 PAH, a diverse group of five- and six-ring PAH, some of which are present at trace levels in the environment. To better understand the mutagenicity of this class of compounds, 11 C24H14 PAH, including benzo[a]perylene, benzo[b]perylene, dibenzo[a,e]fluoranthene, dibenzo[a,f]fluoranthene, dibenzo[j,l]fluoranthene, dibenzo[a,h]pyrene, dibenzo[a,i]pyrene, dibenzo[e,l]pyrene, naphtho[1,2-b]fluoranthene, naphtho[2,3-a]pyrene, and naphtho[2,3-e]pyrene, were tested in a mutagenicity assay based on human h1A1v2 cells. h1A1v2 cells are a line of human B-lymphoblastoid cells that have been engineered to express cytochrome P4501A1 (CYP1A1), an enzyme capable of metabolizing promutagenic PAH. Mutagenicity was measured at the thymidine kinase (tk) locus following a 72-h exposure period. Our results show that nine of the compounds were mutagenic. Benzo[a]perylene, dibenzo[a,e]fluoranthene, dibenzo[a,i]pyrene, and naphtho[2,3-a]pyrene were the most potent mutagens, having minimum mutagenic concentrations (MMC) (i.e., the dose at which the induced response was twice that of the negative controls) in the 1-5 ng/ml range. Benzo[b]perylene, dibenzo[a,h]pyrene, dibenzo[a,f]fluoranthene, and naphtho[2,3-e]pyrene were somewhat less potent mutagens, having MMC in the 10-30 ng/ml range. Dibenzo[e,l]pyrene, which had an MMC of 280 ng/ml, was the least potent mutagen. Dibenzo[j,l]fluoranthene and naphtho[1,2-b]fluoranthene were not mutagenic at the doses tested (1-3000 ng/ml). The most mutagenic compounds were also quite toxic. At the highest doses tested, benzo[a]perylene, dibenzo[a,e]fluoranthene, dibenzo[a,i]pyrene, dibenzo[a,h]pyrene, and dibenzo[a,f]fluoranthene induced > 60% killing, and naphtho[2,3-a]pyrene and naphtho[2,3-e]pyrene induced > 50% killing. Benzo[b]perylene, dibenzo[e,l]pyrene, dibenzo[j,l]fluoranthene, and naphtho[1,2-b]fluoranthene induced < 50% killing at the highest doses tested. Comparing these results to a previous study in which nine other C24H14 PAH were tested for mutagenicity in this same assay, it was found that dibenzo[a]pyrene isomers were generally more mutagenic than the other groups of C24H14 PAH tested. These observations are discussed with emphasis given to identifying C24H14 PAH that may be important environmental mutagens.     

Detection of mutagenic activity in automobile exhaust

Using the Ames Salmonella-microsome system, we detected mutagenic activity in the exhaust from two kinds of 4-cycle gasoline engines of unregulated and regulated cars, and from diesel engines, as well as in the particulates from air collected in tunnels. The mutagenicity of particulates from a car equipped with a catalyst (regulated car), as compared with that from an unregulated car, was reduced very much (down to 500 from 4500 revertants/plate/m3 in tester strain TA98). However, the mutagenicity of the ether-soluble acid and neutral fractions from the condensed water of emissions from a regulated car was still high (down to 2880 from 10 900 revertants/plate/m3 in tester strain TA100). The mutagenic activity of emission exhaust from old diesel car engines was very high; the particulates showed 9140 and 19 600 revertants/plate/m3 from strain TA98 incubated with an activating rat-liver S9 fraction. A small diesel engine of the type used for the generation of electric power or in farm machinery also produced exhaust with highly mutagenic particulates. The mutagenic activity of a methanol extract of particulate air pollutants collected in a highway tunnel showed 39 revertants/plate/m3 toward strain TA98 and 87 toward strain TA100. The ether-soluble neutral fraction yielded 86 revertants/plate/m3 from strain TA98 and 100 from strain TA100. This fraction also contained carcinogenic compounds, including benzo[a]pyrene, benzo[e]pyrene, benz[a]anthracene, benzo[ghi]perylene and chrysene. Very high mutagenic activity was detected, especially in the particulate air pollutants collected at night, in another tunnel on a superhighway: 60-88 revertants/plate/m3 from strain TA100 for the sample collected by day, but 121-238, by night. Night traffic includes many more diesel-powered vehicles compared with gasoline-powered automobiles.     

Relationships between structure of nitrated arenes and their mutagenicity in Salmonella typhimurium; 2- and 2,7-nitro substituted fluorene, phenanthrene and pyrene

In order to elucidate the mechanisms of mutagenic activation of nitroarenes, we studied the relationships between the mutagenic potency and chemical structure of 2-nitro- and 2,7-dinitro-arenes including nitrated fluorene (Fl), dihydrophenanthrene (DHPh), phenanthrene (Ph), tetrahydropyrene (THPy), dihydropyrene (DHPy) and pyrene (Py) together with 9-NO2-Ph, 1-NO2-Py and 1.3-diNO2-Py. The mutagenicity tests were carried out on Salmonella typhimurium TA98, TA98NR and TA98/1,8-DNP6 in the absence of S9 mix. The order of mutability of mononitro- and dinitro-arenes in TA98 is as given below: 2-NO2-THPy less than 2-NO2-Fl less than 2-NO2-DHPh less than 9-NO2-Ph less than 2-NO2-Ph less than 2-NO2-DHPy less than 1-NO2-Py less than 2-NO2-Py, and 2,7-diNO2-DHPh less than 2,7-diNO2-Fl less than 2,7-diNO2-THPy less than 2,7-diNO2-Ph less than 2,7-diNO2-DHPy less than 2,7-diNO2-Py less than 1,3-diNO2-Py. 9-NO2-Ph and 1-NO2-Py, which have been detected in environmental samples, are not as potent mutagens as 2-nitrated phenanthrene and pyrene, respectively. 2-NO2THPy (37.7 rev/nmole) was a weak mutagen, but 2,7-diNO2-THPy (3197 rev/nmole) was as potent a mutagen as 2,7-diNO2 (3925 rev/nmole). Tetrahydropyrene has a twisted form in its structure. 1,3-diNO2-Py (99660 rev/nmole) was more mutagenic than 2,7-diNO2-Py (37960.0 rev/nmole), and their mutagenicities were correlated with the behavior of the K-band in their UV spectra by the introduction of nitro groups on pyrene.     

Mutagenicity and co-mutagenicity of catechol on Salmonella

Catechol was not mutagenic for Salmonella typhimurium TA98, TA100 or TA1537 in the presence or absence of S9 mix. At the lower level of S9 in the Ames method, the mutagenic activity of benzo[a]pyrene decreased with the increased addition of catechol. When catechol was added to the pre-incubation mixture at a higher concentration than in the conventional Ames method, the mutagenic activity of benzo[a]pyrene increased with the increased addition of catechol. Catechol is believed to be a co-mutagen for benzo[a]pyrene in the presence of a sufficient amount of S9 in the incubation mixture.     

Aryl hydrocarbon receptor-mediated activity of mutagenic polycyclic aromatic hydrocarbons determined using in vitro reporter gene assay

Activation of aryl hydrocarbon receptor (AhR) by 30 polycyclic aromatic hydrocarbons (PAHs) was determined in the chemical-activated luciferase expression (CALUX) assay, using two exposure times (6 and 24h), in order to reflect the metabolization of PAHs. AhR-inducing potencies of PAHs were expressed as induction equivalency factors (IEFs) relative to benzo[a]pyrene and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In 24h exposure assay, the highest IEFs were found for benzo[k]fluoranthene, dibenzo[a,h]anthracene and dibenzo[a,k]fluoranthene (approximately three orders of magnitude lower than TCDD) followed by dibenzo[a,j]anthracene, benzo[j]fluoranthene, indeno[1,2,3-cd]pyrene, and naphtho[2,3-a]pyrene. The 6h exposure to PAHs led to a significantly higher AhR-mediated activity than the 24h exposure (generally by two orders of magnitude), probably due to the high rate of PAH metabolism. The strongest AhR inducers showed IEFs approaching that of TCDD. Several PAHs, including some strong mutagens, such as dibenzo[a,l]pyrene, cyclopenta[cd]pyrene, and benzo[a]perylene, elicited only partial agonist activity. Calculation of IEFs based on EC25 values and/or 6h exposure data is suggested as an alternative approach to estimation of toxic potencies of PAHs with high metabolic rates and/or the weak AhR agonists. The IEFs, together with the recently reported relative mutagenic potencies of PAHs [Mutat. Res. 371 (1996) 123; Mutat. Res. 446 (1999) 1] were combined with data on concentrations of PAHs in extracts of model environmental samples (river sediments) to calculate AhR-mediated induction equivalents and mutagenic equivalents. The highest AhR-mediated induction equivalents were found for benzo[k]fluoranthene and benzo[j]fluoranthene, followed by indeno[1,2,3-cd]pyrene, dibenzo[a,h]anthracene, benzo[a]pyrene, dibenzo[a,j]anthracene, chrysene, and benzo[b]fluoranthene. High mutagenic equivalents in the river sediments were found for benzo[a]pyrene, dibenzo[a,e]pyrene, and naphtho[2,3-a]pyrene and to a lesser extent also for benzo[a]anthracene, benzo[b]fluoranthene, indeno[1,2,3-cd]pyrene, benzo[j]fluoranthene, dibenzo[a,e]fluoranthene and dibenzo[a,i]pyrene. These data illustrate that AhR-mediated activity of PAHs, including the highly mutagenic compounds, occurring in the environment but not routinely monitored, could significantly contribute to their adverse effects.     

Genotoxic activity of two furan analogues of benzo[a]pyrene and their 2-nitro derivatives

We measured the genotoxic activities in two bacterial tests, the Salmonella/histidine assay (a reverse mutation assay) and the SOS Chromotest (an assay for SOS induction in E. coli), of two pairs of isomeric furan analogues of benzo[a]pyrene: pyreno[1,2-b]furan (R7490) and pyreno[2,1-b]furan (R7692) and their 2-nitro derivatives, 8-nitro-pyreno[1,2-b]furan (R7489) and 8-nitro-pyreno[2,1-b]furan (R7691). We found that: For all 4 compounds, the responses were correlated in the two tests. For the 2-nitro derivatives, R7489 and R7691, the responses were extremely high, reaching SOS-inducing potencies of 5.2 X 10(3) and 10(5)/nmole in the SOS Chromotest and mutagenic potencies of 6.3 X 10(4) and 3.7 X 10(7) revertants/nmole in the Salmonella/histidine assay (strain TA98), respectively; the responses were only slightly decreased in nitroreductase-deficient strains. The responses to the two pyrenofurans were increased in the presence of an "activating mixture" but were still lower than that to benzo[a]pyrene. In contrast to benzo[a]pyrene and pyreno[2,1-b]furan (R7692), pyreno[1,2-b]furan (R7490) also gave a response in the absence of an "activating mixture". (5) Compounds with the oxygen heteroatom within the "bay region" gave lower responses than their isomers with the oxygen heteroatom outside the "bay region".     

Mutation spectra of smoky coal combustion emissions in Salmonella reflect the TP53 and KRAS mutations in lung tumors from smoky coal-exposed individuals

Nonsmoking women in Xuan Wei County, Yunnan Province, China who use smoky coal for cooking and heating in poorly ventilated homes have the highest lung cancer mortality rate in China, and their lung cancer is linked epidemiologically to their use of smoky coal. The emissions contain 81% organic matter, of which 43% is polycyclic aromatic hydrocarbons (PAHs). Exposure assessment and molecular analysis of the lung tumors from nonsmoking women who use smoky coal strongly indicate that PAHs in the emissions are a primary cause of the elevated lung cancer in this population. Here we have determined the mutation spectra of an extract of smoky coal emissions in Salmonella TA98 and TA100; the extract was not mutagenic in TA104. The extract was 8.7 x more mutagenic in TA100 with S9 than without (8.7 rev/microg versus 1.0 rev/microg) and was >3 x more mutagenic in TA100 than in TA98--consistent with a prominent role for PAHs in the mutagenicity of the extract because PAHs are generally more mutagenic in the base-substitution strain TA100 than in the frameshift strain TA98. The extract induced only a hotspot mutation in TA98; another combustion emission, cigarette smoke condensate (CSC), also induces this single class of mutation. In TA100, the mutation spectra of the extract were not significantly different in the presence or absence of S9 and were primarily (78-86%) GC --> TA transversions. This mutation is induced to a similar extent by CSC (78%) and the PAH benzo[a]pyrene (B[a]P) (77%). The frequency of GC --> TA transversions induced in Salmonella by the extract (78-86%) is similar to the frequency of this mutation in the TP53 (76%) and KRAS (86%) genes of lung tumors from nonsmoking women exposed to smoky coal emissions. The mutation spectra of the extract reflect the presence of PAHs in the mixture and support a role for PAHs in the induction of the mutations and tumors due to exposure to smoky coal emissions.     

Mutagenic activity of methyl-substituted tri- and tetracyclic aromatic sulfur heterocycles

A number of polycyclic aromatic sulfur heterocycles have been identified in coal-derived products and in shale oils. The mutagenic activity of some of these compounds, including dibenzothiophene, benzo[b]naphtho[1,2-d]thiophene, benzo[b]naphtho[2,1-d]thiophene and benzo[b]naphtho[2,3-d]thiophene have been determined using the Salmonella/microsome mutagenicity test. These compounds demonstrated either very weak or no mutagenic activity. The methyl derivatives of each of these four compounds were assayed for mutagenic activity. Salmonella typhimurium TA98 was used as the tester strain. All assays required a rat-liver homogenate metabolic activator. Five of the methylated derivatives, 1-methylbenzo[b]naphtho[1,2-d]thiophene, 3-methylbenzo[b]naphtho[1,2-d]thiophene, 1-methylbenzo[b]-naphtho[2,1-d]thiophene, 6-methylbenzo[b]naphtho[2,1-d]thiophene and 4-methylbenzo[b]naphtho[2,3-d]thiophene demonstrated mutagenic activity. However, activity was observed only at high concentrations of the metabolic activator.     

Photomutagenicity of 16 polycyclic aromatic hydrocarbons from the US EPA priority pollutant list

The photomutagenicity of 16 polycyclic aromatic hydrocarbons (PAHs), all on the United States Environmental Protection Agency (US EPA) priority pollutant list, was studied. Concomitant exposing the Salmonella typhimurium bacteria strain TA102 to one of the PAHs and light (1.1 J/cm2 UVA+2.1 J/cm2 visible) without the activation enzyme S9, strong photomutagenic response is observed for anthracene, benz[a]anthracene, benzo[ghi]perylene, benzo[a]pyrene, indeno[1,2,3-cd]pyrene, and pyrene. Under the same conditions, acenaphthene, acenaphthylene, benzo[k]fluoranthene, chrysene, and fluorene are weakly photomutagenic. Benzo[b]fluoranthene, fluoranthene, naphthalene, phenanthrene, and dibenz[a,h]anthracene are not photomutagenic. These results indicate that PAHs can be activated by light and become mutagenic in Salmonella TA102 bacteria. At the same time, the mutagenicity for all the 16 PAHs was examined with the standard mutagenicity test with 10% S9 as the activation system. Benzo[b]fluoranthene, benzo[k]fluoranthene, chrysene, acenaphthylene, and fluorene are weakly mutagenic, while the rest of the PAHs are not. In general, the photomutagenicity of PAHs in TA102 does not correlate with their S9-activated mutagenicity in either TA102 or TA98/TA100 since they involve different activation mechanisms.     

CP-arene oxides: the ultimate, active mutagenic forms of cyclopenta-fused polycyclic aromatic hydrocarbons (CP-PAHs)

The bacterial mutagenic response (Ames-assay, Salmonella typhimurium strain TA98+/-S9-mix) of a series of monocyclopenta-fused polycyclic aromatic hydrocarbons (CP-PAHs) identified in combustion exhausts, viz. cyclopenta[cd]pyrene (1), acephenanthrylene (2), aceanthrylene (3) and cyclopenta[hi]chrysene (4), is re-evaluated. The mutagenic effects are compared with those exerted by the corresponding partially hydrogenated derivatives, 3,4-dihydrocyclopenta[cd]pyrene (5), 4,5-dihydroacephenanthrylene (6), 1,2-dihydroaceanthrylene (7) and 4,5-dihydrocyclopenta[hi]chrysene (8). It is shown that the olefinic bond of the externally fused five-membered ring of 1, 3 and 4 is of importance for a positive mutagenic response. In contrast, whilst CP-PAH 2 is found inactive, its dihydro analogue (6) shows a weak metabolism-dependent response. The importance of epoxide formation at the external olefinic bond in the five-membered ring is substantiated by the bacterial mutagenic response of independently synthesized cyclopenta[cd]pyrene-3,4-epoxide (9), acephenanthrylene-4,5-epoxide (10), aceanthrylene-1,2-epoxide (11) and cyclopenta[hi]chrysene-4,5-epoxide (12). Their role as ultimate, active mutagenic forms, when CP-PAHs 1, 3 and 4 exhibit a positive mutagenic response, is confirmed. Semi-empirical Austin Model 1 (AM1) calculations on the formation of the CP-arene oxides (9-12) and their conversion into the monohydroxy-carbocations (9a-12a and 9b-12b) via epoxide-ring opening support our results. For 2 and 4, which also possess a bay-region besides an annelated cyclopenta moiety, the calculations rationalize that epoxidation at the olefinic bond of the cyclopenta moiety is favoured.     

Results of the IPCS collaborative study on complex mixtures.

The International Programme on Chemical Safety (IPCS) sponsored a collaborative study to examine the intra- and inter-laboratory variation associated with the preparation and bioassay of complex chemical mixtures. The mixtures selected were National Institute of Standards and Technology (NIST) Standard Reference Materials (SRMs). 20 laboratories worldwide participated in the collaborative trial. The participating laboratories extracted the organic portion of two particulate samples--an air-particulate sample and a diesel-particulate sample--and bioassayed the extracts. The laboratories simultaneously bioassayed a NIST-prepared extract of coal tar and two control compounds (benzo[a]pyrene, and 1-nitropyrene). The bioassay method used was the Salmonella/mammalian microsome plate-incorporation test using strains TA98 and TA100. Study design also allowed for a comparison of sonication and Soxhlet extraction techniques. The mean extractable masses for the air particles and diesel particles were approximately 5% and 17.5%, respectively. The particulate samples were mutagenic in both strains with and without activation in all 20 laboratories. For TA100 the with and without activation slope values for the air particulate were 162 and 137 revertants per mg particles, respectively. For TA98 the respective diesel slope values were 268 and 269. The mutagenicity slope values for the diesel particles ranged from 3090 (TA98, +S9) to 6697 (TA100, +S9) revertants per mg particles. The coal tar solution was negative for both strains when exogenous activation was not used but was mutagenic in both strains with exogenous activation. The benzo[a]pyrene and 1-nitropyrene were used as positive controls and gave results consistent with the literature. This paper provides a complete summary of the data collected during the collaborative study. Companion papers provide further analysis and interpretation of the results.     

Some chloro derivatives of polynuclear aromatic hydrocarbons are potent mutagens in Salmonella typhimurium

A series of chlorinations of some polynuclear aromatic hydrocarbons (PAH) were carried out and the products were tested for mutagenicity on Salmonella typhimurium TA98 and TA100. We conclude that the chlorination of certain PAHs with low mutagenicity, such as pyrene and benzo[e]pyrene, resulted in the formation of two types of product. The chlorination of pyrene was studied in some detail. The major products of this chlorination were chloro-substituted pyrenes. These compounds showed an S9-dependent mutagenicity and were identified as 1-chloro-, 1,6-dichloro-, 1,8-dichloro- and 1,3-dichloropyrene. On tester strain TA100 the mutagenic effect ranged from 1.4 to 14 revertants/nmol, 1,3-dichloropyrene being the most potent of the isomers. Minor products eluting from a chromatograph in a more polar fraction than the major products were also formed. These compounds were less stable than the major products and were identified as pyrene with chloro additions in the 4- and 5-positions, with various chloro substituents at other positions. These minor products showed a high mutagenic effect on Salmonella in the absence of S9. The mutagenic effect on strain TA100 ranged from 10 to 15 revertants per ng which is at least 40 and 4000 times higher than for 1-nitropyrene and pyrenequinones, respectively. These unstable chloro derivatives of pyrene are difficult to analyse chemically because they are easily degraded and give rise to the more stable 4-chloropyrene.     

Mutagenicity of K-region derivatives of 1-nitropyrene; remarkable activity of 1- and 3-nitro-5H-phenanthro[4,5-bcd]pyran-5-one

The mutagenic activities toward S. typhimurium strains TA98 and TA100 of K-region derivatives of 1-nitropyrene and pyrene were determined. The compounds tested were trans-4,5-dihydro-4,5-dihydroxy-1-nitropyrene (Compound 3), trans-4,5-dihydro-4,5-dihydroxypyrene (Compound 4), 1-nitropyrene-4,5-quinone (Compound 5), 1-nitropyrene-9,10-quinone (Compound 6), pyrene-4,5-quinone (Compound 7), and the lactones, 1-nitro-5H-phenanthro[4,5-bcd]pyran-5-one (Compound 8), 3-nitro-5H-phenanthro[4,5-bcd]pyran-5-one (Compound 9), and 5H-phenanthro[4,5-bcd]pyran-5-one (Compound 10). Neither pyrene nor any of its K-region derivatives was mutagenic, either in the absence or presence of S9 mix at the doses tested. Of the K-region derivatives of 1-nitropyrene, the lactones (Compounds 8 and 9) were generally the most active; 0.25 microgram/plate induced 900-2200 revertants in TA98 or TA100 without activation. The 4,5-dihydrodiol (Compound 3), an established mammalian metabolite of 1-nitropyrene, was less mutagenic than was 1-nitropyrene in TA98, but was more mutagenic than was 1-nitropyrene in TA100, regardless of the presence of S9 mix. The quinones (Compounds 5 and 6) were less mutagenic than was 1-nitropyrene in the absence of S9 mix in both strains, but their activities were increased in the presence of S9 mix. The mutagenic activities of the lactones (Compounds 8 and 9) were lower in strains TA98NR and TA98/1,8-DNP6 than in TA98, indicating that nitro-reduction and esterification are involved in their activation. The results of this study indicate that K-region derivatives of 1-nitropyrene may be important in its metabolic activation.