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Cyclopenta[c,d]pyrene: a highly mutagenic polycyclic aromatic hydrocarbon.

A polycyclic aromatic hydrocarbon recently isolated from carbon black and identified as cyclopenta[c,d]pyrene (CPP) is highly mutagenic. By the criteria of the Salmonella/mammalian-microsome mutagenicity test, the mutagenic potency of CPP is equalled by only two other naturally occurring polycyclic aromatic hydrocarbons--benzo[a]pyrene and dibenz[a,c]anthracene. The potent mutagenicity of CPP is noteworthy for two reasons: (i) CPP is a mutagenic polycyclic aromatic hydrocarbon without a "bay-region" and (ii) there is evidence that it is distributed widely in the environment. On the basis of experimental observations and perturbational molecular orbital calculations we propose that a mutagenic metabolite of CPP will be the 3,4-oxide. The carbonium ion derived from opening of CPP 3,4-oxide is identical to that derived from opening of benzo[a]pyrene 7,8-diol-9,10-oxide, the metabolite now thought to be an ultimate mutagenic and carcinogenic species.

Benzopyrenes

[Characteristics of DNA during binding with polycyclic aromatic hydrocarbons in vitro].

Polycyclic aromatic hydrocarbons (PAH) were covalently bound to DNA by means of various activating systems. The following systems were used: the microsomal fraction of the rat liver, the system with I2, the system with ascorbic acid and FeSO4. Breaks in DNA due to the activating systems action appeared in all of these systems. Plateau of the PAH binding system curve in the microsomal system cannot be attributed either to the fall of the PAH metabolism rate to zero, or to the PAH binding sites in DNA. This plateau is the result of equalization of the rates of the two contrary-directed processes: the binding of metabolites and their removal due to DNA degradation. Because of the breaks in DNA caused by the activating systems, the authors failed to discover the changes in sedimentation data of DNA due to the covalently bound PAH.

Ascorbic Acid

Quantum chemical studies of polycyclic aromatic hydrocarbons and their metabolites: correlations to carcinogenicity.

In the context of the bay region hypothesis for polycyclic aromatic hydrocarbon (PAH) carcinogenesis, molecular properties were calculated for seventeen polycyclic aromatic hydrocarbons related to (1) intrinsic substrate reactivities towards activating and detoxifying metabolism and (2) the stabilities of the putative carbocation ultimate carcinogens. All-valence electron methods were used, avoiding the inherent difficulties found in the pi-electron methods. The calculated substrate reactivities were found to predict major metabolites successfully, supporting the validity of their use in attempted correlations with observed carcinogenic potencies. Positive correlations were found between observed carcinogenic potencies and (1) the reactivities of the parent polycyclic aromatic hydrocarbons towards the initial distal bay region epoxidation and (2) the stabilities of the diol epoxide carbocations. The reactivities of the distal bay region diol epoxides, were high for both carcinogenic and non-carcinogenic compounds, implying that the second epoxidation does not determine relative carcinogenic activity. Support for a possible alternative hypothesis, that polycyclic aromatic hydrocarbons are activated by one electron oxidation, was also found.

Carcinogens

Dose-dependent preferential binding of polycyclic aromatic hydrocarbons to reiterated DNA of murine skin cells in culture.

The distribution of active metabolites of polycyclic aromatic hydrocarbons bound to reiterated or unique regions of murine DNA has been studied by a DNA-DNA renaturation technique. Murine skin cells were exposed to different doses of radioactive polycyclic aromatic hydrocarbons for 24 hr; then the hydrocarbon-labeled DNA was isolated, fragmented, and denatured. Renaturation kinetics and thermal stabilities of DNA-DNA duplexes were studied. At high carcinogen doses, polycyclic aromatic hydrocarbon adducts seem to be distributed equally among the DNA of all reiteration frequencies. At low carcinogen doses, however, a dose-dependent preferential binding to reiterated DNA sequences occurs. An inverse linear relationship appears to exist between the enrichment of hydrocarbon adducts in reiterated DNA sequences and the logarithm of the amount of total hydrocarbon bound to DNA.

9,10-Dimethyl-1,2-benzanthracene

Investigation on the carcinogen burden by air pollution in man. XV. Polycyclic aromatic hydrocarbons in automobile exhaust gas--an inventory.

Polycyclic aromatic hydrocarbons (=PAH) emitted by two different vehicles were separated by gas chromatography and characterized by mass spectrometry after enrichment from exhaust gas condensate. Gasoline was investigated also using this technique. The quantities of PAH with boiling points higher than 338 degrees C contained in the exhaust gas were compared to those present in the fuel. About 150 different PAH have been characterized by mass spectrometry, 75 of these were identified by means of comparison with authentic samples. Six compounds of the PAH-group consisting of 4-7 rings, which are suspected of possessing carcinogenic activity, are described here for the first time. Structures of these hitherto unidentified PAH are proposed by means of MS and UV spectral informations (11H-cyclopenta(qrs)benzo(e)-pyrene, 10H-cyclopenta(mno)benzo(a)pyrene, benzo(ghi)cyclopenta(pqr)perylene, cyclopentenopyrene). According to the different PAH-profiles of the fuel and of the exhaust gas, it is concluded that the main part of the PAH emitted is produced de novo during the combustion in the engine and furthermore that the PAH contained in the fuel are combusted for the most part.

Carcinogens

[Method for identifying and determining polycyclic aromatic hydrocarbons in foods, soil and drinking water].

A method is described for identifying and determining polycyclic aromatic hydrocarbons in foods, soil and drinking water that, owing to the combination of extractive, chromatographic and spectrophotometric techniques, permits to detect 0,01 microgram of bezo(a)pyrene/kg in the presence of other polycyclic aromatic hydrocarbons. The preparation, pretreatment and concentration of the samples depend upon their nature. The isolation and separation of the polycyclic aromatic hydrocarbons are achieved with the aid of two consecutive thin-layer chromatographic systems, silica gel and acetylated cellulose. The subsequent identification and determination are based on the ulta-violet spectra (limit of detection, almost 0,5 microgram/ml) and, in the nanogram range, on the in situ fluorescence spectral analysis (limit of detection, 0,005 microgram of benzo(a)pyrene/spot). Fluorescence excitation and emission spectra obtained directly from the acetylated cellulose plate permit not only the reliable identification but also the determination of the polycyclic aromatic hycrocarbons; fluorescence transfer loci obtained under various conditions, the simultaneous determination. Depending upon the kinds of sample material, the recovery values range from 75 to 99.6% with a variation coefficient between 10.3 and 22.1%. Furthermore, a limiting value method is presented that permits to take yes-no decisions, by means of thin-layer chromatographic screening without using complicated measuring techniques, indicating whether or not the respective sample complies with the benzo(a)pyrene standard.

Chromatography, Thin Layer

A bacteriophage system for screening and study of biologically active polycyclic aromatic hydrocarbons and related compounds.

The usefulness of bacterial viruses for detecting substances that are potentially carcinogenic is reexamined as a model system for screening biologically active polycyclic aromatic hydrocarbons. A modification of the original assay procedure allows one to distinguish between aromatics that can modify the biological activity of infectious nucleic acids directly and those polycyclic aromatic hydrocarbons that require metabolic activation by Escherichia coli enzymes. The effect of chemical modification of several different polycyclic aromatic hydrocarbons, with respect to their biological activity in the phage assay system, is described. Among the 31 different compounds examined, (+/-)-anti-benzo[a]pyrene-7,8-diol-9,10-epoxide was the most potent inhibitor of infectious phage nucleic acid. The (+) and (-) isomers of the above racemic mixture did not differ significantly in their capacity to inhibit phage replication.

Benz(a)Anthracenes

The determination of polycyclic aromatic hydrocarbons at the ng/L level in Ottawa tap water.

Samples of Ottawa drinking water, collected in January and February 1978 were analysed by Gas Chromatography/Mass Spectrometry (GC/MS) for fifty polycyclic aromatic hydrocarbons (PAH) and five oxygenated polycyclic aromatic hydrocarbons (O-PAH), following extraction of the organic species using Amberlite XAD-2 macroreticular resin. In the January sample, thirty PAHs, ranging in concentration from 0.05 to 14 ng/L with a mean value of 3.8 ng/L and a total weight of 114 ng/L and four O-PAHs, ranging in concentration from 0.10 to 1.8 ng/L with a mean value of 0.91 ng/L and a total weight of 3.7 ng/L, were detected. In the February sample, thirty-six PAHs, ranging in concentration from 0.05 to 8.1 ng/L with a mean value of 1.4 ng/L and a total weight of 50.4 ng/L and five O-PAHs, ranging in concentration from 0.20 to 2.4 ng/L with a mean value of 1.0 ng/L and a total weight of 5.2 ng/L, were detected. Twenty-eight PAHs and four O-pahs were common to the two samples. The use of Amberlite XAD-2 macroreticular resin to extract PAHs from drinking water is shown to be effective, although the recovery of individual PAHs from artificially loaded XAD-2 resin varied from 57 to 100%.

Chromatography, Gas

An appraisal of relative airborne sub-urban concentrations of polycyclic aromatic hydrocarbons monitored indoors and outdoors.

Particle-size distribution studies of polycyclic aromatic hydrocarbons in city and sub-urban atmospheres indicate that these compounds are associated with particles having MMD values of about 0.5 micrometer. Ambient airborne concentrations of pyrene, chrysene, benzo[a]pyrene, benzo[e]pyrene and coronene at suburban sites between 11 and 17 km from a city centre are shown to be approximately similar inside and outside detached residential houses. At all sites, monitored chrysene appears in highest concentration in the range 4-7 ng m-3, followed by benzo[a]pyrene and benzo[e]pyrene between 2-4 ng m-3, with coronene generally less than 1 ng m-3. By taking benzo[a]pyrene as a typical example of this class of compounds, these results indicate that the lungs of sub-urban populations will be exposed to about 34 ng of benzo[a]pyrene per day. This background amount is roughly equivalent to the exposure to this chemical experienced by the lung when one cigarette is smoked per day.

Air Pollutants

[Profiles of polycyclic aromatic hydrocarbon metabolites after treatment with various inducers of microsomal rat liver monoxygenases (author's transl)].

The microsomal oxidation of 12 frequently occurring environmental polycyclic aromatic hydrocarbons after incubation with rat-liver microsomes has been studied and their metabolites characterized by means of gas-liquid chromatography/mass spectrometry. The method enables the detection and characterisation of phenols, diols, triols, and tetrols as trimethylsilyl ethers beside the original hydrocarbons. Moreover, the induction properties of some carcinogenic and non-carcinogenic hydrocarbons (benz[a]anthracene, pyrene, chrysene, benzo[a]-pyrene, benzo[e]pyrene, benzo[b]fluoranthene, benzo[j]fluoranthene, benzo[k]fluoranthene) have been studied. Except pyrene and benzo[e]pyrene, all compounds investigated significant but different induction factors. The relevance of the induction for an estimation of the biological effect of environmental polycyclic aromatic hydrocarbons is discussed.

Animals

Determination of polycyclic aromatic hydrocarbons in sediments and mussels from Saudafjord, W. Norway, by glass capillary gas chromatography.

Polycyclic aromatic hydrocarbons (PAH) have been determined, by glass capillary gas chromatography, in two species of bivalves (Mytilus edulis and Modiolus modiolus) and sediments of Saudafjorden, Norway. The PAH observed are derived from waste effluents from a ferro alloy smelter. Up to 34 PAH compounds were identified, including some reported to be carcinogenic. The concentrations decreased rapidly with distance from the source and with sediment depth, but could be traced more than 15 km from the source. Relative abundance of various PAH did not change significantly in the mussels collected from the head to the mouth of the fjord. In the sediments, however, phenanthrene increased from minor importance to dominance towards the mouth, whereas the relative content of anthracene and benzo [a]pyrene decreased. The results are compared with observations from other marine localities and discussed in relation to transport processes, biodegradation and chemical transformation in the sediments.

Animals

Mutagenic and carcinogenic properties of polycyclic aromatic hydrocarbons.

The rapid development of the chemical industry, combustion of fossil fuels, and smoking of tobacco have resulted in contact of the general population with benzo(a)pyrene and other carcinogenic aromatic hydrocarbons. Persons especially at risk occupationally are those engaged in thermal processing of oil shale, coal, and heavy residual petroleum. It has been shown that polycyclic aromatic hydrocarbons require metabolic activation before they can act as mutagens or carcinogens. This metabolic activation results from interaction with microsomal enzymes present in many body cells, yielding reactive epoxides which react with DNA and produce mutations in the count frame shift or participate in covalent bounding. While opinions differ regarding the relative role of these processes in mutagenesis, considerable evidence exists which links mutagenesis and carcinogenesis. Metabolites of the polycyclic aromatic hydrocarbons which are carcinogenic are usually mutagenic, which supports the hypothesis that damage to chromosomes plays an important role in carcinogenesis. These facts open the possibility to monitoring the spread of carcinogenic substances in the biosphere by relatively simple tests whose endpoint is mutagenesis.

Air Pollutants

Covalent binding of polycyclic aromatic hydrocarbons to adenine correlates with tumorigenesis in mouse skin.

Mouse epidermal homogenates were utilized to convert various polycyclic aromatic hydrocarbons to metabolites capable of binding covalently with nucleic acids. Poly(G) showed the highest capacity to bind covalently with the hydrocarbons; however, there was no correlation between binding to poly(G) and mouse skin tumorigenicity. On the other hand, covalent binding to poly(A) correlated well with values obtained for binding to DNA and mouse skin tumorigenicity. The order of binding to poly(A) was; 7,12-dimethylbenza[a]anthracene greater than benzo[a]pyrene greater than dibenz[a,h]anthracene greater than dibenz[a,c]anthracene.

9,10-Dimethyl-1,2-benzanthracene

Identification of polycyclic aromatic hydrocarbons in carbon black with reference to cancerogenic risk in tire production.

Carbon blacks used in tire production have been examined for their polycyclic aromatic hydrocarbons (P.A.H.) content. The analytical procedures commonly adopted are discussed. The results obtained show that, A benzene extraction time of 250 hours is necessary to obtain complete extraction, but for practical purposes, an extraction time of 150 hours is sufficient to extract more than 95% of the PAH. It is possible to identify two classes of blacks in regard to extractables. The one class provides extractables in the range of 200--400 micrograms/g; the second class, in the range of 1000--2000 micrograms/g. No P.A.H. were detected by direct injection of carbon black into the mass spectrograph at 200 degrees C, 10(-6) torr. This was probably due to the very strong bonding to the black particles. The P.A.H. contribute a relative constant percentage of the benzene extracts. It is reasonably possible to exclude any carcinogenic risk to personnel, in a working environment, with an airborne carbon black concentration equal to or less than 3.5 mg/m3, due to the very low P.A.H. content of carbon black and to the very strong P.A.H. bonding to the black particles.

Carbon

Regulation of the binding of 7,12-dimethylbenz[a]-anthracene to DNA of cultured murine epidermal cells at metabolic level: competition of the binding by polycyclic aromatic hydrocarbons and by other precarcinogens.

The binding of labeled carcinogen [3H]DMBA to murine epidermal cells (MEC) DNA in culture has been studied. The influence of unlabeled noncarcinogenic and carcinogenic polycyclic aromatic hydrocarbons (PAH), several PAH metablites, and various directly and indirectly acting non-PAH carcinogens on the binding of [3H]DMBA to MEC DNA has been examined. All the carcinogenic PAH and some of non-carcinogenic PAH effectively inhibit the binding of [3H]DMBA to MEC DNA. The non-PAH chemical carcinogens requiring metabolic activation also reduce the binding of labeled DMBA to MEC DNA; however, a higher concentration of these compounds is required for 50% inhibition of binding than the concentrations of PAH for the same degree of inhibition of binding of [3H]DMBA to MEC DNA. The directly acting carcinogens do not significantly inhibit the binding of [3H]DMBA to DNA. The relationship between structures of PAH and their ability to inhibit the binding of [3H]DMBA to MEC DNA is also discussed. Thus, it appears that the binding of DMBA to cellular DNA is primarily controlled at a level of metabolism and to some extent at the level of binding of reactive metabolites to DNA.

9,10-Dimethyl-1,2-benzanthracene

Determination and identification of polycyclic aromatic hydrocarbons in smoked and charcoal-broiled food products by high pressure liquid chromatography and gas chromatography.

A high pressure liquid chromatographic procedure has been developed and applied to the analysis of polycyclic aromatic hydrocarbons (PAH's) in 70 samples of smoked food products commercially available in Canada, and in 6 charcoal broiled meats. In some cases a gas-liquid chromatographic procedure was used as a confirmatory technique. In the commercial samples PAH's were detected in approx. 70% of the samples. Total PAH's ranged from 0-141 ppb and individual PAH's from 0-38 ppb. With the charcoal-broiled samples, total PAH's and individual PAH's ranged from 0-164 ppb and 0-60 ppb respectively. These levels are similar to those observed in other countries.

Canada

Factors affecting the binding of polycyclic aromatic hydrocarbons to human embryo cells, and transformable and non-transformable hamster embryo cells.

The effects of various factors, including population doubling number, percent of confluence, serum concentration and storage in liquid nitrogen on the binding of several polycyclic aromatic hydrocarbons to human and hamster embryo cells were studied. The binding of 7,12-dimethylbenz[a]-anthracene (DMBA) to hamster embryo cells DNA, RNA and protein was maximal after 22 h of treatment. In contrast, binding to human embryo cell macromolecules increased for at least 55 h. Treatment of hamster embryo cells at 100% confluence resulted in much less binding than treatment at 70% confluence, whereas with human embryo cells the binding increased, or remained constant, following treatment at the greater confluence. The transforming frequency of hamster embryo cells decreases with increasing population doubling number. Accordingly, we found that the binding of DMBA to hamster embryo DNA, RNA and protein decreased approximately 100-fold between population doubling numbers 8 and 20. In transformable cell cultures, DMBA was bound to hamster embryo cell DNA to a greater extent than to RNA or protein. The binding of DMBA to nucleic acids was much greater than binding by either dibenz[a,h]anthracene (DB[a,h]A) or dibenz-[a,c]anthracene (DB[a,c]A), both of which had low binding values at all population doubling numbers tested. Therefore, the best correlation of binding with carcinogenicity and transforming activity was observed with DMBA. Storage of hamster embryo cells in liquid nitrogen did not alter their binding characteristics. Binding of all three hydrocarbons to human embryo cell nucleic acids was low during all population doubling numbers studied, while binding to cellular protein increased until population doubling number 70 and then decreased sharply.

9,10-Dimethyl-1,2-benzanthracene