Reaction of methyl methanesulphonate with nucleic acids of fetal and newborn rats in vivo

Developmental toxicity of dimethyl sulfate by inhalation in the rat

Dimethyl sulfate (DMS; CAS No. 77-78) is a colorless, oily liquid which is used as a chemical intermediate and as a reactant in producing polyurethane resins. In this study, groups of pregnant Crl:CD BR rats were exposed, nose-only, to either 0.1, 0.7 or 1.5 ppm DMS by inhalation for 6 hr/day from Days 7 through 16 of gestation (day in which copulation plug was detected was designated Day 1G). A control group of pregnant rats was exposed simultaneously to air only. All female rats were euthanized on Day 22G and the fetuses were examined. A suppression of both food consumption and the rate of body weight gain was seen in the 0.7 and 1.5 ppm groups. No unusual clinical signs were seen in rats exposed to DMS. None of the reproductive parameters was altered in any of the groups and no statistically significant fetal effects were detected. DMS is not a developmental toxin in the rat following inhalation exposures up to 1.5 ppm during the period of major organogenesis.

Comparison of DNA alkylation, fragmentation, and repair in maternal and fetal tissues of pregnant rats treated with a single dose of ethyl methanesulfonate, ethyl-N-nitrosourea, N-nitrosodiethylamine, and methyl-N-nitrosourea

The occurrence and persistence of DNA damage, as detected by the alkaline elution technique, have been studied in some tissues of both fetal and adult Sprague-Dawley rats (18th day of gestation) after administration of a single equimolar dose (0.5 mmol/kg) of ethyl methanesulfonate (EMS), N-ethyl-N-nitrosourea (ENU), N-nitrosodiethylamine (NDEA), and N-methyl-N-nitrosourea (MNU). EMS, ENU, and MNU, injected intravenously, produced a statistically significant increase of DNA elution rate, which is considered indicative of DNA fragmentation, in both maternal and fetal liver, kidney, and brain. NDEA, introduced by gastric gavage, induced DNA breaks in both liver and kidney of dams, but only in the liver of fetuses. The frequency of DNA lesions was found to vary with the four alkylating agents and in the three organs tested, to exhibit a different time course, and usually to be higher in maternal than in fetal tissues. Results provided by the concomitant determination of DNA binding levels demonstrated a satisfactory correlation with the amounts of DNA fragmentation. In contrast, the values of both these parameters did not show any positive correlation with the different susceptibility of the three organs to tumor induction. In conclusion, these findings suggest that when a compound is not available in radiolabeled form, measurement of DNA fragmentation may represent a useful alternative to the determination of DNA binding level in order to obtain information on the distribution of its reactive species in maternal and fetal tissues.

In vivo covalent binding of organic chemicals to DNA as a quantitative indicator in the process of chemical carcinogenesis

The covalent binding of chemical carcinogens to DNA of mammalian organs is expressed per unit dose, and a 'Covalent-Binding Index', CBI, is defined. CBI for various carcinogens span over 6 orders of magnitude. A similar range is observed for the carcinogenic potency in long-term bioassays on carcinogenicity. For the assessment of a risk from exposure to a carcinogen, the total DNA dmaage can be estimated if the actual dose is also accounted for. A detailed description is given for planning and performing a DNA-binding assay. A complete literature survey on DNA binding in vivo (83 compounds) is given with a calculation of CBI, where possible, 153 compounds are listed where a covalent binding to any biological macromolecule has been shown in vivo or in vitro. Recent, so far unpublished findings with aflatoxin M1, macromolecule-bound aflatoxin B1, diethylstilbestrol, and 1,2-epithiobutyronitrile are included. A comparison of CBI for rat-liver DNA with hepatocarcinogenic potency reveals a surprisingly good quantitative correlation. Refinements for a DNA-binding assay are proposed. Possibilites and limitations in the use of DNA binding in chemical carcinogenesis are discussed extensively.

The chemical and biochemical reactivity of dichlorvos

The chemical structure, reactivity and metabolic fate of the insecticide dichlorvos (2,2-dichlorovinyl dimethyl phosphate) are discussed in relation to the possible genotoxicity of this and other methyl phosphate triesters. Recent attempts to demonstrate the methylation of DNA following exposure of bacteria and animals to dichlorvos are reviewed. On the basis of comparative data relating mutagenesis to methylation reactions, it seems entirely appropriate to conclude that the mutagenicity of dichlorvos to bacteria is due solely to methylation of the bacterial DNA under the conditions of these tests. However, the methylation of mammalian DNA could not be demonstrated under realistic exposure conditions (when the alkylating mutagen methyl methanesulphonate afforded clearly measurable methylation). The failure to detect methylation by dichlorvos in vivo is attributed to the operation of highly efficient enzyme-catalysed biotransformations which rely largely on the phosphorylating reactivity of dichlorvos. The biotransformation pathways, characterised mostly in the rat, appear to be common also to pig, mouse, hamster, and man.