Analysis of mutagens by the microsuspension forward-mutation assay in Salmonella typhimurium strain TM677.
Explore the source record for details and available documents.
Biomedical subjects
Publications and source records attributed to L Claxton.
Explore the source record for details and available documents.
The development of short-term genetic bioassays has made it possible to conduct mutagenicity studies on complex mixtures of indoor air pollutants. Although most of the studies have used the standard S. typhimurium/microsome reversion assay developed by Ames et al. (1975), the development of microsuspension mutagenesis methods (see Methods 18 and 19, this volume) has facilitated wider use of bioassays in indoor air pollution studies. It is clear from the studies reviewed here that environmental tobacco smoke is the major source of mutagens indoors. Other sources which produce significant, but much smaller, increases in indoor air mutagenicity include outdoor air and other indoor combustion sources (e.g., cooking, kerosene heaters and open fireplaces burning wood). These studies have been based on measurement of the bacterial mutagenicity of extracts from particulate matter. A limited number of reports, however, indicate that volatile and semi-volatile constituents of indoor air may also be mutagenic and deserve further study.
Urine from cigarette smokers was analyzed for the effect upon mutagenic activity when stored for as long as 175 days. Frozen aliquots of urine were thawed out at various time points in the study and prepared for bioassay. These urine extracts were not bioassayed immediately, but rather refrozen until all of the unprocessed urine samples had eventually been prepared for bioassay. All extracts were obtained using cyanopropyl solid phase extraction techniques. At the end of 175 days, all extracts were bioassayed using a microsuspension assay of Salmonella typhimurium TA98. Urine from smokers was found to be mutagenic (14.4-30.9 revertants/ml equivalent) while a control set of urine from non-smokers was not. Data from the storage study when analyzed by analysis of variance techniques indicated no statistical loss of mutagens occurred over the 175-day period although near significance was observed (P = 0.054). This near significance was the result of decreasing mutant response as storage time increased for two of the higher doses tested.
A variety of linear and nonlinear mathematical models have been proposed to characterize Salmonella mutagenicity data sets, but no systematic procedure has been suggested for comparing two or more data sets across experiments, laboratories, occasions, mutagens or treatment conditions. In this paper, a general method for data-set comparison is provided. Nonlinear regression techniques are applied to real data sets. Data-set and parameter equivalence are described in depth. Confidence-band construction for nonlinear models and other graphical techniques are presented as auxiliary tools. Key Statistical Analysis System (SAS) code programs are provided.
Urine from cigarette smokers was prepared for mutagenicity testing by extracting mutagens with solid-phase extraction columns. Commercially available prepacked bonded silicas (octadecyl, cyclohexyl, cyanopropyl) were compared for their ability to concentrate the urinary mutagens. Recovered urinary metabolites were evaluated for mutagenic activity by using a microreversion assay with Salmonella typhimurium. Dose-response data indicated that while mutagens were recovered by all three adsorbents, samples prepared by using the bonded cyanopropyl columns yielded the most bioactivity and/or the least amount of test organism toxicity. Varying pH of the urine was found to influence only the basified samples in terms of mutagenic recovery with the cyanopropyl base. Combinations of different adsorbents were not found to offer significant advantages over use of a singular extraction adsorbent.
Two dyes (C.I. Solvent Yellow No. 33 and a mixture of C.I. Solvent Yellow No. 33 and C.I. Solvent Green No. 3) were tested for mutagenicity in the Salmonella reversion assay and the L5178Y/TK+/- mouse lymphoma assay, and also for sister chromatid exchange (SCE) induction in vivo in C57B1/6J mice. In addition, a greater than 99.9% pure sample of the yellow dye [2-(2'-quinolyl)-1,3-indandione] was tested with and without exogenous activation in the Salmonella reversion assay and the L5178Y/TK+/- mouse lymphoma assay. Neither C.I. Solvent Yellow No. 33 nor the C.I. Solvent Yellow No. 33 and Solvent Green No. 3 mixture was positive for inducing SCEs in vivo. All three dyes were tested in the standard plate incorporation test in seven Salmonella strains TA98, TA100, TA102, TA104, TA1535, TA1537, and TA1538. The dyes were negative with and without exogenous activation in TA98, TA1535, and TA1538. One test with TA1537 was positive with the greater than 99.9% purified yellow dye. All three dyes gave weakly positive results (less than a twofold increase) with S-9 in TA100 and were clearly positive in TA102 and TA104 both with and without S-9. They also induced mutation at the thymidine kinase locus in mouse lymphoma cells, produced both large- and small-colony trifluorothymidine-resistant mutants, and were clastogenic. The purified yellow dye was further tested for SCE induction in mouse lymphoma cells and was determined to give a slightly positive response in the presence of S-9.
The microsomal metabolites and mutagenic activity of four cyclopenta-fused benz(a)anthracenes, benz(j)aceanthrylene [B(j)A], benz(e)aceanthrylene [B(e)A], benz(l)aceanthrylene [B(l)A], and benz(k)acephenanthrylene [B(k)A], have been studied. Aroclor 1254-induced rat liver microsomes metabolized B(j)A to B(j)A-1,2-dihydrodiol, B(j)A-9,10-dihydrodiol, B(j)A-11,12-dihydrodiol, and 10-hydroxy-B(j)A; B(e)A-1,2-dihydrodiol, B(e)A-3,4-dihydrodiol, and B(e)A-5,6-dihydrodiol; B(l)A to B(l)A-1,2-dihydrodiol, B(l)A-4,5-dihydrodiol, and B(l)A-7,8-dihydrodiol; and B(k)A to B(k)A-4,5-dihydrodiol and B(k)A-8,9-dihydrodiol. With each polycyclic aromatic hydrocarbon, metabolism occurred on the cyclopenta ring. All four isomers were active as gene mutagens in Salmonella typhimurium and in Chinese hamster V79 cells. In the S. typhimurium mutation studies, using Aroclor 1254-induced rat liver S9, B(j)A, B(e)A, and B(l)A required significantly less microsomal protein for maximal mutation response than B(k)A and B(a)P, suggesting a one-step activation mechanism, presumably on the cyclopenta-fused ring. B(j)A, B(e)A, and B(l)A were significantly more mutagenic than B(k)A and B(a)P in S. typhimurium. In the Aroclor 1254-induced rat liver S9-mediated V79 mutagenesis system, all four isomers were active, with B(l)A the most active. When Syrian hamster embryo cells were used as the metabolic activation component for V79 cells, only B(l)A produced a significant response and was equivalent in activity to B(a)P. A helical configuration for B(l)A is inferred from the identification of two trans-B(l)A-1,2-dihydrodiols, syn and anti, which have been synthesized, separated, and characterized. The metabolically formed dihydrodiol is anti-trans-B(l)A-1,2-dihydrodiol, and experimental evidence suggests that the metabolically formed B(l)A-1,2-oxide is the anti-isomer. Synthetic B(l)A-1,2-oxide was found to be a direct-acting mutagen in S. typhimurium and Chinese hamster V79 cells and is estimated to account for up to 40% of the mutagenic activity of the parent hydrocarbon. Therefore, certain cyclopenta-ring fusions on benz(a)anthracene appear to markedly increase its genotoxic and carcinogenic activities.
The mutagenic activities of 1-nitropyrene (1-NP), 2,7-dinitrofluorenone (2,7-DNF), and a diesel-exhaust extract were compared using the Salmonella typhimurium plate-incorporation assay. Each sample was tested with and without a 9000 X g liver homogenate (S9), both with and without an NADPH-generating system. The samples were also treated with the microsome fraction of S9, cytosol fraction of S9, boiled S9, bovine serum albumin (BSA), and boiled BSA. Salmonella tester strains TA98 and TA98FR1 were used in all treatments; TA98/1,8DNP6 was used to test mutagenic activity without activation. Without the NADPH-generating system, the samples generally had less mutagenic activity than samples treated with the NADPH-generating system. The addition of the NADPH-generating system resulted in marked increases in mutagenic activity of 1-NP in the microsome and S9 treatments, and of all 3 samples in the cytosol fraction treatment. These results indicate that although protein binding reduced the mutagenic activity of diesel-exhaust extract and 1-NP, microsomal activation increased the mutagenic activity of 1-NP. Because 1-NP and 2,7-DNF contributed less than 1.5% of the mutagenic activity of the diesel-exhaust extract, the response to diesel exhaust was not typified by these compounds.
Initial studies on the mutagenicity and metabolism of a novel cyclopenta-PAH, benz[j]aceanthrylene, are reported in the Salmonella bacterial system. The spectrum of activity of benz[j]aceanthrylene over the 5 Ames tester strains is similar to that of benzo[a]pyrene, and the dose-response curves for strain TA98 are comparable. Like other biologically active PAH, benz[j]aceanthrylene is a frame-shift mutagen requiring metabolic activation. An interesting feature of the S9 dependence of activity is the low concentration (congruent to 10-fold smaller than for benzo[a]pyrene) at which optimal activity is observed. The 1,2-dihydro-1,2-diol (product of metabolism of the cyclopenta-ring) appears to be the predominant metabolite, and implicates the 1,2-oxide as the ultimate mutagenic species.
Despite the value and widespread use of the Ames test, little attention has been focused on standardizing quantitative methods of analyzing these data. In this paper, a realistic and statistically tractable model is developed for the evaluation of Ames-type data. The model assumes revertant colony formation at any dose follows a Poisson process, while the mean number of revertants per plate is a nonlinear function of up to 4 parameters. An exponential decay term can be included in the model to adjust for toxicity. The resultant system of nonlinear equations is solved using a modified Gauss-Newton iterative scheme to obtain maximum likelihood estimates of the model parameters. Significance of the key parameters is tested by fitting reduced models and using likelihood ratio tests. The model's performance is demonstrated on data from organic extracts of various environmental contaminants. Among the advantages of the proposed model are (1) no data is discarded in the parameter estimation process, (2) no arbitrary constants need to be added to zero counts or doses, and (3) no mathematical transformation of the data is required.
Explore the source record for details and available documents.
Explore the source record for details and available documents.
Twenty laboratories worldwide participated in a collaborative trial sponsored by the International Programme on Chemical Safety on the mutagenicity of complex mixtures as expressed in the Salmonella/microsome assay. The U.S. National Institute of Standards and Technology provided homogeneous reference samples of urban air and diesel particles and a coal tar solution to each participating laboratory, along with samples of benzo[a]pyrene and 1-nitropyrene which served as positive controls. Mutagenic potency was characterized by the slope of the initial linear component of the dose-response curve. Analysis of variance revealed significant interlaboratory variation in mutagenic potency, which accounted for 57-96% of the total variance on a logarithmic scale, depending on the sample, strain and activation conditions. Variation among replicate extractions of organic material (required for the air and diesel particles) and among replicate bioassays within the same laboratory was also appreciable. The average potencies for air and diesel particles in laboratories using Soxhlet extracts were not significantly different from those in laboratories using sonication, although there was larger interlaboratory variation for the Soxhlet method. Repeatability (which approximates the coefficient of variation within laboratories) ranged from 18 to 40% for air and diesel particles extracted using sonication, depending on the strain and activation conditions. Repeatability of Soxhlet-extracted air and diesel particles, however, ranged from about 37 to 89% including outliers and from about 11 to 31% excluding outliers. Repeatability of the coal tar sample and the 2 positive controls was in the range 18-34%. Reproducibility (which approximates the coefficient of variation between laboratories) was generally at least twice repeatability, and exceeded 100% for Soxhlet-extracted air and diesel particles, as well as 1-nitropyrene. Reanalysis of the data omitting observations of more than 1500 revertants/plate generally had little effect on these results. Elimination of outlying observations had limited impact, with the exception of Soxhlet-extracted air and diesel particles. In this case, reproducibility of bioassay results was notably improved, due largely to the omission of results for replicate extractions which varied more than 5-fold within one laboratory. Normalization of the log potency slopes for the mixtures by the corresponding slopes for benzo[a]pyrene tended to reduce this variation, although variation was increased after normalization by 1-nitropyrene. Adjustment for the percentage of organic matter extracted from the air and diesel particulate samples had little effect on variation for sonication-extracted particles, whereas variation was reduced for diesel particles and increased for air particles for Soxhlet.