Mutagenicity of polycyclic hydrocarbons. II. Monitoring genetical hazards of chrysene in vitro and vivo.

Mutagenicity tests were performed with chrysene in the Salmonella/microsome test, NMRI-mice oocytes, bone-marrow cells and spermatogonia of Chinese hamsters. Only in mice oocytes was a weak but significant increase of structural chromosome aberrations observed. Correlations were found between weak carcinogenic and observed weak mutagenic activities of chrysene in vitro and in vivo.     

Mutagenicity and K-region reactivity of monomethyl derivatives of benz(a)anthracene in a self-consistent-field molecular orbital theory

The relative mutagenicities of the monomethyl derivatives of benz(a)anthracene have been studied on the basis of their K-region reactivities as obtained from a suitable self-consistent-field molecular orbital theory for the mobile π-electrons. Barring a few specific cases of these monomethyl derivatives, a nice correlation between the mutagenicities and the K-region reactivities has been obtained.     

Mutagenicity of non-K-region diols and diol-epoxides of benz(a)anthracene and benzo(a)pyrene in S. typhimurium TA 100

When incubated with a 9,000 x g rat-liver supernatant, benzo(a)pyrene 7,8-diol and benz(a)anthracene 8,9-diol were more active than the parent hydrocarbons in inducing his⁺ revertant colonies of S. typhimurium TA 100. Benzo(a) pyrene 9,10-diol was less active than benzo(a)pyrene; the K-region diols, benz(a)anthracene 5,6-diol and benzo(a)pyrene 4,5-diol, were inactive. None of the diols was active when the cofactors for the microsomal mono-oxygenase were omitted. The diol-epoxides benzo(a)pyrene 7,8-diol 9,10-oxide, benz(a)anthracene 8,9-diol 10,11-oxide and 7-methylbenz(a)anthracene 8,9-diol 10,11-oxide and the K-region epoxides, benzo(a)pyrene 4,5-oxide and benz(a)anthracene 5,6-oxide, were mutagenic without further metabolism.     

The presence of the mutagenic polycyclic aromatic hydrocarbons benzo[a]pyrene and benz[a]anthracene in creosote P1

Several fractions of creosote P1 separated by TLC showed mutagenicity towards Salmonella typhimurium TA98. Thus mutagenicity is probably caused by the presence of mutagenic aromatic hydrocarbons. The mutagenic polycyclic aromatic hydrocarbons, benzo[a]pyrene and benz[a]anthracene, were detected in concentrations of 0.18 and 1.1% respectively. Because these compounds are probably not essential for the wood-preserving properties of creosote , a more selective composition of the product should be considered.     

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.     

Bacterial oxidation of chemical carcinogens: formation of polycyclic aromatic acids from benz[a]anthracene.

A Beijerinckia strain designated strain B1 was shown to oxidize benz[a]anthracene after induction with biphenyl, m-xylene, and salicylate. Biotransformation experiments showed that after 14 h a maximum of 56% of the benz[a]anthracene was converted to an isomeric mixture of three o-hydroxypolyaromatic acids. Nuclear magnetic resonance and mass spectral analyses led to the identification of the major metabolite as 1-hydroxy-2-anthranoic acid. Two minor metabolites were also isolated and identified as 2-hydroxy-3-phenanthroic acid and 3-hydroxy-2-phenanthroic acid. Mineralization experiments with [12-14C]benz[a]anthracene led to the formation of 14CO2. These results show that the hydroxy acids can be further oxidized and that at least two rings of the benz[a]anthracene molecule can be degraded.     

In-vitro induction of vegetative buds by benz(a)anthracene in tobacco callus

Summary Benz(a)anthracene induced vegetative buds on callus derived from stem tissue of haploid plants of Nicotiana tabacum a response similar to that obtained by a combination of kinetin and IAA.This study was carried out under Contract No. 12-14-100-10278 (5) with the Agricultural Research Service, U.S. Department of Agriculture, administered by the Eastern Utilization Research and Development Division, Philadelphia.     

Bacterial oxidation of chemical carcinogens: formation of polycyclic aromatic acids from benz[a]anthracene

A Beijerinckia strain designated strain B1 was shown to oxidize benz[a]anthracene after induction with biphenyl, m-xylene, and salicylate. Biotransformation experiments showed that after 14 h a maximum of 56% of the benz[a]anthracene was converted to an isomeric mixture of three o-hydroxypolyaromatic acids. Nuclear magnetic resonance and mass spectral analyses led to the identification of the major metabolite as 1-hydroxy-2-anthranoic acid. Two minor metabolites were also isolated and identified as 2-hydroxy-3-phenanthroic acid and 3-hydroxy-2-phenanthroic acid. Mineralization experiments with [12-14C]benz[a]anthracene led to the formation of 14CO2. These results show that the hydroxy acids can be further oxidized and that at least two rings of the benz[a]anthracene molecule can be degraded.     

Mutagenicity of benzylic acetates, sulfates and bromides of polycyclic aromatic hydrocarbons

Studies were performed to determine the direct mutagenicity of the acetates and some bromides and sulfates of hydroxymethyl polycyclic aromatic hydrocarbons in S. typhimurium strains TA98 and TA100. Benzylic acetates, bromides and sulfates were synthesized and characterized. The compounds tested were benzyl alcohol, 5-hydroxymethylchrysene, 1-hydroxymethylpyrene, 6-hydroxymethylbenzo[a]pyrene, 6-(2-hydroxyethyl)benzo[a]pyrene, 6-hydroxymethylanthanthrene, 9-hydroxymethylanthracene, 9-hydroxymethyl-10-methylanthracene, 7-hydroxymethylbenz[a]anthracene, 7-(2-hydroxyethyl)benz[a]anthracene, 12-hydroxymethylbenz[a]anthracene, 7-hydroxymethyl-12-methylbenz[a]anthracene, 12-hydroxymethyl-7-methylbenz[a]anthracene, 1-hydroxy-3-methylcholanthrene, 2-hydroxy-3-methylcholanthrene, 3-hydroxy-3, 4-dihydrocyclopental[cd]pyrene and 4-hydroxy-3, 4-dihydrocyclopental[cd]pyrene. The benzylic sulfate esters of 6-hydroxymethylbenzo[a]pyrene and 7-hydroxymethylbenz[a]anthracene were the most mutagenic compounds, whereas the aliphatic sulfate ester of 7-hydroxyethylbenz[a]anthracene did not cause an increase in mutations above background. All meso-anthracenic benzylic acetate esters were mutagenic in both strains with various degrees of activity, whereas the corresponding non-benzylic esters were inactive, as expected. Of the non-meso-benzylic acetate esters, only the 3-acetoxy-3, 4-dihydrocyclopenta[cd]pyrene was mutagenic. In the benzylic bromide series, only the eight mesoanthracenic were mutagenic, whereas benzyl bromide and 5-bromomethylchrysene were inactive. The aliphatic bromides, 6-(2-bromoethyl)benzo[a]pyrene and 7-(2-bromoethyl)benz[a]anthracene did not display significant activity. The potencies of the acetate esters more accurately reflect the mutagenicity because the rate of solvolysis did not compete with the reactivity of the esters with bacterial DNA. In the case of benzylic sulfates and bromides, the rate of solvolysis was very rapid and could have diminished the level of mutagenicity, depending on the assay conditions. These results demonstrate that meso-anthracenic benzylic acetates, sulfates and bromides are mutagenic, whereas benzylic acetate esters attached to other carbon atoms are inactive.     

Metabolic and stereoselective formations of non-K-region benz(a)anthracene 8,9- and 10,11-epoxides

The non-K-region benz[a]anthracene (BA) 8,9- and 10,11-epoxides were isolated by normal-phase high-performance liquid chromatography as rat liver microsomal metabolites of BA. The identities of these epoxides were established by ultraviolet and mass spectral analyses and were further validated by the microsomal epoxide hydrolase catalyzed conversion to BA trans-8,9-dihydrodiol and trans-10,11-dihydrodiol, respectively. Circular dichroism spectral analyses of the metabolically formed non-K-region epoxides and dihydrodiols and mass spectral analyses of metabolically formed 18O-labeled non-K-region dihydrodiols and their acid-catalyzed dehydration products indicated that BA (8R,9S)-epoxide and (10S,11R)-epoxide were the predominant enantiomers formed in the metabolism at the 8,9- and 10,11- aromatic double bonds of BA, respectively, by rat liver microsomes. This is the first example demonstrating the direct detection and stereoselective metabolic formation of non-K-region epoxides of a polycyclic aromatic hydrocarbon.     

Mutagenicity of a series of hexacoordinate cobalt(III) compounds

15 cobalt(III) compounds have been tested for DNA-damaging capabilities using an E. coli differential repair assay and for mutagenicity in strains of Salmonella typhimurium. 4 of these compounds were active in both systems. Although the general ligand requirements for genetic activity of cobalt(III) appear to closely parallel those of chromium(III) and rhodium(III), the genetic activity of cobalt compounds seems particularly dependent upon the structure of the ligands coordinated about the metal ion. By a simple methyl substitution on the organic ligands, a compound completely devoid of activity, e.g. trans-[Co(pyr)4Cl2]Cl, could be made slightly mutagenic in Salmonella typhimurium strains e.g. trans-[Co(3-pic)4Cl2]Cl. Substitution at the 4-position rather than the 3-position on the same pyridine ring, e.g. trans-[Co(4-pic)4Cl2]Cl, results in a 50-fold enhancement of activity in both repair and mutagenesis systems. The difference in genetic activity is attributed to the influence of the ligands on the relative lability of the metal complex.     

Mutagenicity and polycyclic aromatic hydrocarbons analysis of airborne particulate matters from Taipei City

The mutagenic activity of dichloromethane extracts of 147 air particulate samples collected from 8 stations during December 1986-June 1987 in Taipei city was consistently higher in S. typhimurium strain TA 98 than in strain TA 100 in the presence of S9 mixture. Among the 8 stations, Nan Kang Police Station, Fu Hsing Elementary School, and Chung Hsing University which were located in the industrial district, downtown area, and heavy traffic zone, respectively, had significantly higher levels of PAHs than the other stations. In contrast, the levels of PAHs were much lower in the suburban station, near Pei Tou Elementary School. However, PAH contents of the air particulate samples collected from these stations did not show good correlation with their mutagenicity. The air particulates collected at some stations on Sunday when the traffic changed from heavy to light showed lower mutagenicity and PAH contents as compared with the other weekdays at the same stations. On the contrary, the samples collected at Pei Tou station in a suburban area where the traffic changed from light to heavy on Sunday showed higher mutagenicity and PAH contents. The monthly average of PAHs of air particulate samples collected over a 7-month period from 8 stations in Taipei city was lower than the average in 1980. Moreover, when compared with other countries, such as U.S.A., the Netherlands, West Germany, Italy, Norway, and Japan, the levels of PAHs and mutagenicity of air particulate matters in Taipei city were similar or slightly lower. The mutagenicity and contents of PAHs of air particulates collected from burnt ABS were significantly higher than those of burnt PVC. One sample PT-6-3 was collected while a nearby garbage collection area was on fire. The mutagenicity of that sample increased 3 to 16 fold and contained an 11 to 33 times higher content of the six PAHs (BaP, BeP, BbF, BaA, Chr, and DbA) as compared with the other samples collected at the same location at a different time. The higher mutagenicity and PAH contents of that sample might be due to the pollution of the air from combustion of the garbage containing products made of ABS.     

Glass-capillary-gas chromatography/mass spectrometry data of mono- and polyhydroxylated benz[a]anthracene. Comparison with benz[a]anthracene metabolites from rat liver microsomes

By means of glass-capillary-gas chromatography all possible benz[a]anthracene metabolites formed by rat liver microsomes (phenols, dihydrodiols, dihydrodiol enols and tetrahydrotetrols) can be separated. Mass spectra of their trimethylsilyl ethers show intense molecule ions and, in most cases, characteristic fragments. K-Region diols and their secondary oxidation products can be recognized by the ratio (m/e 147) (m/e 191) greater than 1, whereas the ratio is inverse in all other dihydrodiol trimethylsilyl ethers investigated. With the exception of 1,2-dihydrobenz[a]anthracene-1,2,3-triol all vicinal dihydrodiol enols investigated exhibit an intense elimination of the fragment CH = CH-OSiMe3 according to m/e 379. The conformation of vicinal tetrahydrobenz[a]anthracenetetrols possibly can be distinguished by the intensity of m/e 380 (M - 240) since only in those possessing two or more subsequent Me3SiO groups in the same conformation intense elimination of Me3Si-O-CH = CH-O-SiMe3 is observed. Retention times and mass spectrometric data of a series of synthetic benz[a]anthracene derivatives are presented as a base for the identification of benz[a]anthracene metabolites in biological systems.     

Fluorescence and photoelectron studies of the intercalative binding of benz(a)anthracene metabolite models to DNA

An analog of the peptidyl transferase inhibitor sparsomycin was a competitive inhibitor (Ki = 1.8 microM) of peptidyl-puromycin synthesis on E. coli polysomes. Preincubation of polysomes with the compound enhanced the degree of inhibition of peptide bond formation. A model for the involvement of a histidine residue in peptidyl transferase activity is presented as a result of our observations which include direct association of [3H] labelled analog with 70S ribosomes. The correct oxidation state of sulfur in the compound was necessary for the preincubation effect and entry of the compound into bacterial cells.     

Metabolism of benz[a]anthracene by the filamentous fungus Cunninghamella elegans.

The metabolism of the carcinogen benz[a]anthracene (BA), a tetracyclic aromatic hydrocarbon, by Cunninghamella elegans was investigated. C. elegans grown on Sabouraud dextrose broth transformed [14C]BA to labeled BA trans-8,9-dihydrodiol (90%), BA trans-10,11-dihydrodiol (6%), and BA trans-3,4-dihydrodiol (4%), but not to BA trans-5,6-dihydrodiol. These metabolites were separated by thin-layer chromatography and reversed-phase high-performance liquid chromatography and were identified by UV and mass spectral techniques. A BA tetraol, 8 beta,9 alpha,10 alpha,11 beta-tetrahydroxy-8 alpha, 9 beta,10 beta,11 alpha-tetrahydro-BA, was also identified as a metabolite and may have arisen as an additional oxidation product of either BA 8,9- or 10,11-dihydrodiol. This is the first study in which a biologically produced BA tetraol has been identified. Our results suggest that the transformation of BA to trans-dihydrodiols by C. elegans is similar to the transformation of BA found in mammals, except that BA 5,6-dihydrodiol is not produced.