1,3-Butadiene is a major industrial chemical that has been shown to be a carcinogen at multiple sites in mice and rats at concentrations as low as 6.25 ppm. Occupational exposures have been reduced in response to these findings, but it may not be possible to determine by using traditional epidemiological methods, whether current exposure levels are adequate for protection of worker health. However, it is possible to evaluate the biological significance of exposure to genotoxic chemicals at the time of exposure by measuring levels of genetic damage in exposed populations. We have conducted a pilot study to evaluate the effects of butadiene exposure on the frequencies of lymphocytes containing mutations at the hypoxanthine-guanine phosphoribosyl transferase (hprt locus in workers in a butadiene production plant. At the same time, urine specimens from the same individuals were collected and evaluated for the presence of butadiene-specific metabolites. Eight workers from areas of the plant where the highest exposures to butadiene occur were compared to five workers from plant areas where butadiene exposures were low. In addition, six subjects with no occupational exposure to butadiene were also studied as outside controls. All of the subjects were nonsmokers. An air sampling survey conducted for 6 months, and ending about 3 months before the study, indicated that average butadiene levels in the air of the high-exposure areas were about 3.5 ± 7.5 ppm. They were 0.03 ± 0.03 ppm in the low-exposure areas. Peripheral blood lymphocytes from the subjects were assayed using an autoradiographic test for hprt mutations. The weighted mean variant (mutant) frequency (Vf) (± SE) in the eight exposed subjects was 3.84(±0.70) x 106 per evaluatable cell, as compared to 1.16±(0.27) x 104 in the low-exposed and 1.03(±0.07) x 106 in the outside controls. The Vf of the low-exposed controls and the outside controls were not significantly different, but the mean frequency of mutant lymphocytes in the seven exposed subjects was significantly higher when compared to the mean Vf of the nonexposed controls (p<0.01) and the low-exposed controls (p<0.05). A single metabolite of butadiene, 1,2-dihydroxy-4-(N-acetlylcysteinyl-S) butane, was detected in the urine of all subjects. The concentration in the urine of the workers in the high-exposed group was significantly greater than in the low-exposed or nonexposed groups. The correlation between the level of the metabolite in urine and the frequency of hprt mutants was r = 0.85. The observation of an elevated Vf in the exposed subjects and the strong correlation of Vf with the level of excreted metabolite suggests that butadiene exposures under these conditions were sufficient to induce somatic cell mutations. This degree of increase in Vf is similar to what we have observed in cigarette smokers. The results available at this time indicate that current levels of occupational exposure to butadiene may not be sufficiently low to protect workers from the adverse effects that may result from exposure...

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The mutations in a series of leucine auxotrophs isolated after treatment with nitrosoguanidine, ultraviolet light, and ICR-191 have been mapped between ilvC and pheA on the Bacillus subtilis chromosome. A fine structure map of the region was constructed by transformation. Analysis of several strains by assaying levels of their leucine bioysnthetic enzymes has shown that the region encodes three enzymes. The order of the genes with respect to the biosynthetic steps catalyzed by the gene products is 1–3–2.

1,3-Butadiene (BD) is a major commodity chemical used in the manufacture of synthetic rubber and various plastics and has been shown to be a potent animal carcinogen and a probable human carcinogen. The bioactivation of BD to reactive epoxides, and the balance between activation and detoxication of these reactive metabolites, is thought to play a critical role in the genotoxic and carcinogenic effects of BD. The detoxication of reactive BD metabolites involves enzymatic conjugation with glutathione by glutathione S-transferases (GSTs) and by hydrolysis, a reaction mediated by microsomal epoxide hydrolase (mEH). Since polymorphisms in genes of xenobiotic-metabolizing enzymes such as mEH may influence individual susceptibility to adverse health effects from BD exposure, we tested the hypothesis that the mEH Tyr113His polymorphism increases sensitivity to the genotoxic effects of BD in exposed workers. We used the autoradiographic hprt mutant lymphocyte assay as a biomarker of effect to identify genotoxicity associated with BD exposure in 49 workers from two styrene/butadiene polymer plants in Southeast Texas. Exposure to BD was assessed by collecting breathing zone air samples using passive badge dosimeters for three full 12 h work shifts 25, 20 and 14 days before blood was collected for genotyping and for the hprt assay. We genotyped the study participants for the Tyr113His polymorphism in the mEH gene and also for deletion polymorphisms in the glutathione S-transferase genes, GSTM1 and GSTT1, as potential biomarkers of susceptibility to BD. Our data indicate that the majority of the study subjects (67%) were exposed to very low levels of BD of <150 parts per billion (p.p.b.) time-weighted average (TWA). In some workers, however, we found levels of BD exposures that exceeded a TWA of 2000 p.p.b. Our data indicate a significant (P < 0.05) 2-fold increase in frequencies of hprt variant (mutant) lymphocytes (Vf) in workers exposed to >150 p.p.b. BD, compared with workers exposed to<150 p.p.b. There was no significant effect from individual GSTM1, GSTT1 or mEH genotypes in workers exposed to <150 p.p.b. BD. In workers exposed to >150 p.p.b., individuals with at least one polymorphic mEH His allele (His/His or His/Tyr genotypes) had a significant (P < 0.001) 3-fold increase in Vf (mean Vf x 10(-6) +/- SE = 13.25 +/- 1.78) compared with individuals with the Tyr/Tyr genotype (mean Vf x 10(-6) +/- SE = 4.02 +/- 0.72). There was no significant effect from individual GSTM1 or GSTT1 polymorphisms, but combined polymorphism analysis showed that the genetic damage was highest in individuals who had at least one mEH His allele and either the GSTM1 and/or GSTT1 null genotypes (hprt Vf = 14.19 +/- 2.30 x10(-6)). In contrast, this response was not observed in individuals exposed to levels of BD < 150 p.p.b. These results indicate that polymorphisms in the mEH gene may play a significant role in human sensitivity to the genotoxic effects of BD exposure, and that the hprt mutant lymphocyte assay can serve as a sensitive biomarker of...

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The National Toxicology Program has recently classified 1,3-butadiene (BD) as a human carcinogen. BD is metabolized to the intermediates 1,2-epoxy-3-butene (EB), 1,2:3,4-diepoxybutane (DEB), and 1,2-dihydroxy-3,4-epoxybutane. All three metabolites have been implicated in producing specific types of DNA damage and as genotoxic agents in mice, rat, and human cells. This study has focused on EB-induced N1 deoxyinosine lesions that are formed by deamination of deoxyadenosine following reaction of the epoxide at the N(1) position. The R and S stereoisomers of this lesion were incorporated site-specifically within the context of an 11-mer oligodeoxynucleotide, incorporated into M13mp7L2 single-stranded DNA, and transfected into E. coli. Both stereoisomers modestly reduced plaque-forming ability, indicating that neither lesion presents a base modification that cannot be bypassed. The resulting plaques were assessed for point mutations using differential hybridization and DNA sequence analyses. The overall mutagenic spectrum revealed that the N1 adducts were highly mutagenic (approximately 90% per replication cycle), causing a predominance of A --> G transitions.