Assessment of the genotoxic effects of methyl chloride in human lymphoblasts

Qualitative analysis of surgical smoke produced during burn operations

Burned tissue is necrotic and it is surrounded by a zone of stasis and hyperaemia with changed cell metabolism. The removal of burned tissue using an electric knife releases large amounts of surgical smoke. The aim of the research was to analyse volatile, nonpolar, organic compounds that are released during the excision of burned tissue using an electric knife (mono- and bipolar). The study includes analysis from 40 solid-phase microextraction (SPME) fibres, exposed during 10 interventions (6 escharotomy and 4 necrectomy). The analysis of volatile compounds was performed using mass spectrometry gas chromatography (GCxGC-ToFMS).The total analysis covered 432 compounds, whereas after the removal of the "background" compounds - 153 volatile organic substances remained. The analysis of surgical smoke showed that, including derivatives, benzene constituted as much as 17.65% of all of the studied compounds. Cyclic compounds constituted on average 22.5% of the analysed substances, out of which cycloheptatrien constituted 20.26%. Alkanes, alcohols and their derivatives constituted nearly 25% of volatile organic compounds, with chloromethane constituting as much as 13.7%. Permutational multivariate analysis of variance (PERMANOVA) revealed statistically significant differences between escharotomy and necrectomy patients (F(1.9) = 5.91, p = 0.007).Our study revealed the presence of complex toxic hydrocarbon derivatives in surgical smoke. We also observed that the content of surgical smoke is different depending on the type of the conducted intervention. So far, no studies focusing on hazards posed by surgical smoke that is released during the resection of burned tissue are in the literature.

A core in vitro genotoxicity battery comprising the Ames test plus the in vitro micronucleus test is sufficient to detect rodent carcinogens and in vivo genotoxins

In vitro genotoxicity testing needs to include tests in both bacterial and mammalian cells, and be able to detect gene mutations, chromosomal damage and aneuploidy. This may be achieved by a combination of the Ames test (detects gene mutations) and the in vitro micronucleus test (MNvit), since the latter detects both chromosomal aberrations and aneuploidy. In this paper we therefore present an analysis of an existing database of rodent carcinogens and a new database of in vivo genotoxins in terms of the in vitro genotoxicity tests needed to detect their in vivo activity. Published in vitro data from at least one test system (most were from the Ames test) were available for 557 carcinogens and 405 in vivo genotoxins. Because there are fewer publications on the MNvit than for other mammalian cell tests, and because the concordance between the MNvit and the in vitro chromosomal aberration (CAvit) test is so high for clastogenic activity, positive results in the CAvit test were taken as indicative of a positive result in the MNvit where there were no, or only inadequate data for the latter. Also, because Hprt and Tk loci both detect gene-mutation activity, a positive Hprt test was taken as indicative of a mouse-lymphoma Tk assay (MLA)-positive, where there were no data for the latter. Almost all of the 962 rodent carcinogens and in vivo genotoxins were detected by an in vitro battery comprising Ames+MNvit. An additional 11 carcinogens and six in vivo genotoxins would apparently be detected by the MLA, but many of these had not been tested in the MNvit or CAvit tests. Only four chemicals emerge as potentially being more readily detected in MLA than in Ames+MNvit--benzyl acetate, toluene, morphine and thiabendazole--and none of these are convincing cases to argue for the inclusion of the MLA in addition to Ames+MNvit. Thus, there is no convincing evidence that any genotoxic rodent carcinogens or in vivo genotoxins would remain undetected in an in vitro test battery consisting of Ames+MNvit.

Toxicology of methyl bromide

Methyl bromide is widely used as an insecticidal fumigant in food supplies, warehouses, barges, buildings, and furniture. Its popularity as a fumigant is largely attributable to its high toxicity to many pests, the variety of settings in which it can be applied, its ability to penetrate the fumigated substances, and its rapid dissipation following application. Because of its frequent use around humans and human-related activities and its high acute toxicity, methyl bromide-related fatal accidents have occurred. The primary route for human exposure to methyl bromide is inhalation. In California, the most frequent cause of death from methyl bromide exposure in recent years has been unauthorized entry into structures under fumigation. The most frequently reported lesions included pulmonary edema, congestion, and hemorrhage. In recent years, a great deal of effort has been given to the characterization of the toxicity of methyl bromide because of its commercial value and its direct and indirect economic importance. Methyl bromide is acutely very toxic. Subchronically and chronically, the principal target site for methyl bromide appears to be the central nervous system. However, there was no evidence for carcinogenic activity of methyl bromide following the normal environmental exposure routes of inhalation or oral intake through residue on foods. Methyl bromide is clearly genotoxic in vitro and in vivo, as evidenced by the positive results from various tests. The mechanism of toxicity for methyl bromide is currently uncertain, although its alkylating property as well as the possibility of forming a reactive intermediate through metabolic transformation remain attractive hypotheses.

Sister-chromatid exchange: second report of the Gene-Tox Program

This paper reviews the ability of a number of chemicals to induce sister-chromatid exchanges (SCEs). The SCE data for animal cells in vivo and in vitro, and human cells in vitro are presented in 6 tables according to their relative effectiveness. A seventh table summarizes what is known about the effects of specific chemicals on SCEs for humans exposed in vivo. The data support the concept that SCEs provide a useful indication of exposure, although the mechanism and biological significance of SCE formation still remain to be elucidated.

Induction of the adaptive response of Escherichia coli to alkylation damage by the environmental mutagen, methyl chloride

Methyl chloride (MeCl) is an abundant environmental mutagen and carcinogen and may be one of several environmental alkylating agents against which the protection of an adaptive response is required in microorganisms. Both MeCl and methyl iodide (MeI), at micromolar concentrations, induced the adaptive response to alkylation damage in Escherichia coli. This response is regulated by the Ada protein which is converted into a transcriptional activator by self-methylation on repair of methylphosphotriesters in methylated DNA. However, using high amounts of Ada protein, activation of Ada occurred in vitro following direct protein methylation by both MeI (in agreement with previously published data) and MeCl. Activation was enhanced when methyl halide treatments were performed in the presence of DNA. An unadapted E. coli cell contains only 2 to 4 molecules of Ada protein, and presents an extremely small target of 2 to 4 specific cysteine residues per cell for activation of Ada by direct protein methylation in vivo. Thus, it is proposed that induction of the adaptive response in vivo initially occurs via efficient repair by the Ada protein of a low number of methylphosphotriesters in DNA. When the cellular Ada protein level has substantially increased, a greater probability of direct methylation and activation of Ada at cysteine-69 by MeCl may sustain and further increase induction of the adaptive response.

Mechanisms of carcinogenicity of methyl halides

Methyl chloride, bromide, and iodide are used as methylating agents. These compounds are mutagenic in short-term tests and do not require activation by exogenous S9 mix. In DNA-binding studies performed in rats and mice, 14C-labeled methyl chloride was given by inhalation, and methylation of DNA bases was examined. The compound did not lead to specific DNA adducts. In particular, methylation of DNA bases was not observed. In contrast, methyl bromide and methyl iodide, upon oral and inhalation administration to rats and mice, caused systemic DNA methylation. Specifically, 3-methyl-adenine, 7-methyl-guanine, and O6-methyl-guanine were formed. Long-term inhalation bioassays have been performed in rats and mice with methyl chloride and methyl bromide. Methyl chloride induced renal tumors, but only in male mice at the highest concentration tested (1000 ppm). Under these special conditions, a number of secondary effects occur subsequent to glutathione depletion in the target tissue, resulting in DNA damage (DNA-protein cross-links and probably DNA single-strand breaks). The particular coincidence of secondary high-dose effects precludes a risk extrapolation to man. Methyl bromide did not induce tumors in rats and mice when administered by inhalation. However, experimental data point to a possible local carcinogenic effect on the rat forestomach when the compound is given by gavage. A factor that accounts for the discrepancy between systemic DNA methylation and apparent noncarcinogenicity upon inhalation might be the preference of 7-N over O6 methylation of guanine. An extrapolation of the negative rodent inhalation bioassay of methyl bromide to man might be problematic because rodents metabolize methyl bromide very quickly whereas in humans there is a particular subpopulation that only poorly metabolizes the compound ("nonconjugators"). Such individuals can be characterized by incubation of erythrocytes with methyl chloride or methyl bromide and measurement of the substrate decline. Methyl iodide has been tested, with positive outcome, in early carcinogenicity bioassays not based on modern methodology. However, these results, along with the proven systemic methylating potency of methyl iodide, argue in favor of a carcinogenic effect of the compound.

Widespread adaptive response against environmental methylating agents in microorganisms

Many bacterial species have adaptive responses which protect against the toxicity and mutagenicity of methylating agents. Induced 3-methyladenine-DNA glycosylase and O6-methylguanine-DNA methyltransferase activities increase the cellular capacity of E. coli, B. subtilis, and M. luteus to repair toxic and mutagenic methylated base derivatives in DNA. The DNA methyltransferase or Ada protein of E. coli regulates the response and is converted into a strong transcriptional activator by self-methylation on repair of a methylphosphotriester in DNA. The multiple functions of the E. coli Ada protein (39 kDa) are split between two proteins, AdaA (24 kDa) and AdaB (20 kDa), in B. subtilis. Proteins (39 kDa) recognised by anti-Ada antibodies are efficiently induced in several enterobacterial species and correlate with increased DNA methyltransferase activities. In contrast, an "Ada-related" protein is only weakly induced in Salmonella typhimurium and no increase in DNA repair activity is detectable. The existence of adaptive responses in diverged bacterial species suggests the frequent occurrence of methylating agents in the environment. Several direct-acting methylating agents which are known to arise in the environment have been shown to induce the response. These include abundantly occurring methyl chloride, the antibiotic streptozotocin, the precursors of the known labile inducers N-methyl-N'-nitrosourea and N-methyl-N'-nitro-N-nitrosoguanidine and as shown in this paper, methyl radicals which may arise by the irradiation or oxidation of methyl compounds.

Role of epididymal inflammation in the induction of dominant lethal mutations in Fischer 344 rat sperm by methyl chloride

This study assessed the possible relationship between methyl chloride (MeCl)-induced epididymal inflammation and the formation of dominant lethal mutations in sperm of Fischer 344 rats. Groups of 40 males were exposed to MeCl (3000 ppm 6 hr/day for 5 days), with or without concurrent treatment with the anti-inflammatory agent 3-amino-1-[m-(trifluoromethyl)phenyl]-2-pyrazoline (BW 755C; 10 mg/kg, i.p. 1 hr pre- and postexposure); BW 755C was shown previously to inhibit MeCl-induced epididymal inflammation. Control groups (n = 20) were either untreated, injected as described above with BW 755C, or injected on the afternoon of day 5 with triethylenemelamine (0.2 mg/kg), a known dominant lethal mutagen. Each male was caged with one female weekly for 3 weeks; 12-18 days after mating, females were killed to assess dominant lethal parameters. In females bred to MeCl-exposed males, significant increases were observed in postimplantation loss at postexposure week 1 (0.84 dead implants per female vs. 0.29 in untreated controls) and in dead implants/total implants at both week 1 (0.10 vs. 0.04 control) and week 2 (0.24 vs. 0.06 control). These increases were not observed in females bred to males treated with BW 755C during MeCl exposure. Coadministration of BW 755C to males along with MeCl also reduced the percentage of mated females with two or more postimplantation losses from 31% to 8% (week 1) and 30% to 12% (week 2). Therefore, the dominant lethal mutations induced by MeCl appear to be a consequence of its induction of inflammation in the epididymis. These data demonstrate the potential genotoxicity of inflammatory processes in vivo.

Inhibition of the acute toxicity of methyl chloride in male B6C3F1 mice by glutathione depletion

Previous data have demonstrated that methyl chloride (MeCl) is toxic to B6C3F1 mice under both acute and chronic exposure conditions, and that conjugation of MeCl with glutathione (GSH) is a key step in the metabolism of MeCl. This study examined the role of GSH in mediating the acute toxicity of MeCl to liver, kidney, and brain of male B6C3F1 mice. The lethal effects of a single 6-hr inhalation exposure of B6C3F1 males to 2500 ppm MeCl were completely prevented by pretreatment with the GSH synthesis inhibitor, L-buthionine-S,R-sulfoximine (4 mmol L-BSO/kg, ip 1.5 hr prior to MeCl exposure). GSH levels (measured as nonprotein sulfhydryl) in liver and kidney were depleted to 19 and 25% of control values, respectively, at the start of the exposure; the ratio of dead/exposed mice during the 18-hr postexposure declined from 14/15 mice to 0/10. Also, the LC50 for MeCl increased from 2200 to 3200 ppm in male mice pretreated with BSO. The hepatic toxicity of MeCl was detected by increased alanine aminotransferase (ALT) activities in serum 18 hr after a 6-hr exposure to 1500 ppm MeCl (2147 +/- 1327 IU/liter vs 46 +/- 6 in controls). Liver toxicity was inhibited when B6C3F1 males were depleted of GSH prior to MeCl exposure by BSO pretreatment (43 +/- 2), fasting (100 +/- 47), or injection of diethyl maleate (42 +/- 16). The effects of GSH depletion on MeCl toxicity to brain and kidney were determined in B6C3F1 males exposed to 1500 ppm MeCl 6 hr/day, 5 days/week for 2 weeks, with and without daily pretreatment with 2 mmol L-BSO/kg. This dose of BSO depleted hepatic and renal GSH by 28 and 60%, respectively, at the start of MeCl exposure. BSO-pretreated mice were protected from the central nervous system toxicity of MeCl, as assessed by microscopic examination of the granule cell layer of the cerebellum. BSO pretreatment also inhibited the renal toxicity of MeCl as measured by incorporation of [3H]thymidine ([3H]TdR) into renal DNA, an indicator of cell regeneration after cortical necrosis. [3H]TdR incorporation was 105 +/- 10,337 +/- 40, and 60 +/- 15 dpm/microgram DNA in nonexposed controls, MeCl, and MeCl + BSO treatment groups, respectively. These results indicate that GSH is an important component in the toxicity of MeCl to multiple organ systems in B6C3F1 mice. Reaction of MeCl with GSH appears to constitute a mechanism of toxication, contrary to the role usually proposed for GSH in detoxifying xenobiotics.

Failure of fertilization as a cause of preimplantation loss induced by methyl chloride in Fischer 344 rats

Methyl chloride (MeCl) is a testicular and epididymal toxicant in the Fischer 344 rat that induces significant decreases in sperm quality in males and significant increases in preimplantation embryonic loss in females mated to exposed males. This study examined the possibility that these losses are due to failure of fertilization and not to preimplantation embryonic death. Groups of males either were exposed to 1000 or 3000 ppm MeCl 6 hr/day for 5 days or received a single ip injection of 0.2 mg/kg triethylenemelamine (TEM) on Day 5 and were bred to two females weekly for up to 8 weeks. Females were killed 12 hr postmating; embryos and ova were isolated and scored as fertilized or unfertilized. Nearly 90% (602/683) of the normal ova recovered from females bred to control males were fertilized, and fertilization rates in the 1000-ppm MeCl and TEM groups were not significantly depressed from that level. The percentage of fertilized ova in the 3000-ppm MeCl group was significantly decreased, ranging from 3 to 72% over the 8 weeks. The frequency of unfertilized ova in this group always equaled or exceeded the frequency of preimplantation loss recorded in an earlier dominant lethal assay. In contrast, only a fraction of the preimplantation losses caused by the genotoxicant TEM could be accounted for by failure of fertilization. After culture of fertilized ova for 24 hr, only the TEM group exhibited a significant decrease in the number of fertilized ova which cleaved (85 vs 96% in the control). We conclude that the preimplantation loss caused by MeCl exposure is due to failure of fertilization and not to a genotoxic effect of MeCl. The methods used here permit a more accurate assessment of the reproductive toxicity of a chemical by discriminating between its cytotoxic and genotoxic effects.

Inhibition of methyl chloride toxicity in male F-344 rats by the anti-inflammatory agent BW755C

This study examined the effectiveness of the cyclooxygenase/lipoxygenase inhibitor 3-amino-1-[m-(trifluoromethyl)phenyl]-2-pyrazoline (BW755C) in preventing the toxicity induced in male F-344 rats by methyl chloride (MeCl). BW755C (10 mg/kg ip, 1 hr pre and postexposure) prevented both lethality (0/6 vs 8/12 in controls) and epididymal granuloma formation (0/6 vs 4/4 in controls) in rats exposed to 7500 ppm MeCl 6 hr/day for 2 days. Additional rats (n = 5 per group) were exposed to 5000 ppm MeCl 6 hr/day for 5 days, with and without BW755C treatment as described above. The rats were killed on Day 5 and tissues processed for light microscopic examination. MeCl-exposed rats showed hepatocellular cloudy swelling, degeneration of renal proximal convoluted tubules, vacuolar degeneration in the adrenal cortex, necrosis of the internal granular layer of the cerebellum, and degenerative changes in the testis and epididymis, including formation of epididymal sperm granulomas. With the exception of the adrenal, tissues examined in rats of the MeCl/BW755C treatment group showed virtually no histologic evidence of lesions. BW755C did not significantly alter metabolism of [14C]MeCl to 14CO2 or 14C in urine, nor did it affect the distribution to various organs of radioactivity derived from [14C]MeCl. Therefore, BW755C protection against MeCl toxicity did not appear to result from altered MeCl metabolism or disposition. Instead, the protection was apparently related to the pharmacologic activity of BW755C as an inhibitor of leukotriene and prostaglandin synthesis.

Unscheduled DNA synthesis in rat tracheal epithelial cells, hepatocytes and spermatocytes following exposure to methyl chloride in vitro and in vivo

Measurement of DNA repair as unscheduled DNA synthesis (UDS) in vitro following exposure in vivo in multiple tissues from the same treated animal can provide valuable information relating to the tissue- and organ-specificity of chemically induced DNA damage. UDS was evaluated in primary cultures of rat tracheal epithelial cells, hepatocytes and pachytene spermatocytes after exposure in vitro to methyl chloride (MeCl), and after isolation from the same treated animal following inhalation exposure in vivo. Concentrations of 1-10% MeCl in vitro induced UDS in hepatocytes and spermatocytes, but not in tracheal epithelial cells. Inhalation exposure to MeCl in vivo (3000-3500 ppm 6 h/day for 5 successive days) failed to induce DNA repair in any cell type. In vivo exposure to 15 000 ppm MeCl for 3 h also failed to induce UDS in tracheal epithelial cells and spermatocytes, but did cause a marginal increase in UDS in hepatocytes. Thus, MeCl appears to be a weak, direct-acting genotoxicant. While activity could be measured in hepatocytes and spermatocytes directly in vitro, only extremely high concentrations of MeCl elicited a response in the whole animal, and then only in hepatocytes.

Assessment of the genotoxic potential of unleaded gasoline and 2,2,4-trimethylpentane in human lymphoblasts in vitro

The potential of unleaded gasoline and 2,2,4-trimethylpentane to induce gene locus mutation and sister-chromatid exchange in human lymphoblasts in vitro was determined. Neither unleaded gasoline, at its maximum tolerated concentration in the medium, nor 2,2,4-trimethylpentane, at its limit of solubility, induced mutation at the thymidine kinase locus. Negative results were seen both in the presence and absence of a rat liver homogenate metabolizing system. Sister-chromatid exchange analyses of the cultures treated with unleaded gasoline and 2,2,4-trimethylpentane were also negative. Therefore the carcinogenicity and nephrotoxicity of unleaded gasoline and 2,2,4-trimethylpentane observed in vivo are not correlated with any marked genotoxicity in these in vitro tests.