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We report the first use of green fluorescent protein (GFP) for mutation detection. We have constructed a plasmid-based bacterial system whereby mutated cells fluoresce and non-mutated cells do not fluoresce. Fluorescence is monitored using a simple hand-help UV lamp; no additional cofactors or manipulations are necessary. To develop a reversion system, we introduced a +1 DNA frameshift mutation in the coding region of GFP and the resulting protein is not fluorescent in Escherichia coli. Treatment of bacteria containing the +1 frameshift vector with ICR-191 yields fluorescent colonies, indicating that reversion to the wild-type sequence has occurred. Site-directed mutagenesis was used to insert an additional cytosine into a native CCC sequence in the coding region of GFP in plasmid pBAD-GFPuv, expanding the sequence to CCCC. A dose-related increase in fluorescent colonies was observed when the bacteria were treated with ICR-191, an agent that induces primarily frameshift mutations. The highest dose of ICR-191 tested, 16 microg/ml, produced a mutant fraction of 16 x 10(-5) and 8.8 x 10(-5) in duplicate experiments. The reversion system did not respond to MNNG, an agent that produces mainly single-base substitutions. To develop a forward system, we used GFP under the control of the arabinose PBAD promoter; in the absence of arabinose, GFP expression is repressed and no fluorescent colonies are observed. When cells were treated with MNNG or ENNG, a dose-dependent increase in fluorescent colonies was observed, indicating that mutations had occurred in the arabinose control region that de-repressed the promoter. Treating bacteria with 100 microg/ml MNNG induced mutant fractions as high as 82 x 10(-5) and 40 x 10-5 in duplicate experiments. Treating bacteria with 150 microg/ml ENNG induced a mutant fraction of 2.1 x 10(-5) in a single experiment., (Copyright 1998 Elsevier Science B.V.)

Trichloroethylene (TCE) (CAS No. 79-01-6) is an industrial solvent used in degreasing, dry cleaning, and numerous other medical and industrial processes. Controlled inhalation studies were performed using male C57BL/6 mice and CD rats to determine if TCE can induce cytogenetic damage in vivo. Animals were exposed in groups of five to target concentrations of either 0, 5, 500, or 5000 ppm TCE for 6 h. Tissue samples were taken between 18 and 19 h post exposure. Peripheral blood lymphocytes (PBLs) in rats and splenocytes in mice were cultured and analyzed for the induction of sister-chromatid exchanges, chromosome aberrations, and micronuclei (MN) in cytochalasin B-blocked binucleated cells. Bone marrow polychromatic erythrocytes (PCEs) were analyzed for MN. The only positive response observed was for MN in rat bone marrow PCEs. TCE caused a statistically significant increase in MN at all concentrations, inducing an approximate fourfold increase over control levels at 5000 ppm. TCE was also cytotoxic in rats, causing a significant concentration-related decrease in the ratio of PCEs/normochromatic erythrocytes. This study indicates that there may be species-specific cytogenetic effects attributed to TCE inhalation exposure. In follow-up studies, CD rats were exposed for 6 h/day over 4 consecutive days to either 0, 5, 50 or 500 ppm TCE. No statistically significant concentration-related increases in cytogenetic damage were observed. While the MN frequencies in the 4-day study were comparable to those at the equivalent concentrations in the 1-day study, they were not significantly elevated due to an unusually high MN frequency in the controls. A subsequent replication of the 1-day 5000 ppm TCE exposure with rats again showed a highly significant increase in MN frequencies compared to concurrent controls.

Male Fischer 344 rats and female B6C3F1 mice were each exposed through their drinking water to a mixture of pesticides and ammonium nitrate that simulated contaminated groundwater in California (California Chemical Mixture [CCM]). Exposures were for 71 or 91 days, respectively. In addition, B6C3F1 female mice were exposed for 91 days to another pesticide and ammonium nitrate mixture (Iowa Chemical Mixture [ICM]) through their drinking water. The spleens were removed from the animals, and the splenocytes were cultured for analyses of sister-chromatid exchange (SCE), chromosome aberrations (CA), and micronuclei (MN) in cytochalasin B-induced binucleate cells. A concentration-related increase in SCEs was found in the splenocytes of the rat at the 1x, 10x and 100x levels of the CCM and at the 100x concentration of the CCM in the mouse. There were no other consistent cytogenetic effects observed with the CCM, and no statistically significant cytogenetic damage was observed in mice exposed to the ICM. Evidence from the literature is discussed in order to infer which chemical or chemicals in the CCM might be responsible for the observed SCE response.

The data for the in vivo genotoxicity of styrene (STY) are equivocal. To evaluate the clastogenicity and sister-chromatid exchange (SCE)-inducing potential of STY in vivo under carefully controlled conditions, B6C3F1 female mice were exposed by inhalation for 6 h/day for 14 consecutive days to either 0, 125, 250 or 500 ppm STY. One day after the final exposure, peripheral blood, spleen, and lungs were removed and cells were cultured for the analysis of micronucleus (MN) induction using the cytochalasin B-block method, chromosome breakage, and SCE induction. Peripheral blood smears were also made for scoring MN in erythrocytes. There was a significant concentration-related elevation of SCE frequency in lymphocytes from the spleen and the peripheral blood as well as in cells from the lung. However, no statistically significant concentration-related increases were found in the frequency of chromosome aberrations in the cultured splenocytes or lung cells, and no significant increases in MN frequencies were observed in binucleated splenocytes or normochromatic erythrocytes in peripheral blood smears.

The present study was designed to investigate the genotoxicity of 4-hydroxycyclophosphamide (4-OHCP) and phosphoramide mustard (PAM), both reactive metabolites of cyclophosphamide (CP), for possible differences in SCE-inducing activity in mouse T- and B-lymphocytes. Mouse peripheral blood lymphocytes were isolated and stimulated to divide with either phytohemagglutinin (T-cell mitogen) or lipopolysaccharide (a polyclonal B-cell activator). Significant concentration-dependent increases in SCE frequencies were observed for both 4-OHCP and PAM with both mitogens, with 4-OHCP being almost twice as potent as PAM. There was no difference in SCE response between T- and B-lymphocytes after exposure to either PAM or 4-OHCP. These data do not support the idea that the difference in SCE response in T- and B-lymphocytes by CP in vivo is due to differential responses to either of the proposed putative metabolites of CP.