In vivo alkylation studies with dichlorvos at practical use concentrations

Guanine N7-alkylation in mice in vivo by metrifonate - discussion of possible genotoxic risk in mammals

Following intraperitoneal administration to male mice (strain AB Jena/Halle) of 14CH3-labelled metrifonate, 22 Ci/mol, in dosages of 0.48, 0.40 and 0.065 mmol/kg, DNA from liver and kidneys was analysed for 14C in N-7 methylguanine (7-MeG). The extent of methylation in liver was found to be maximal at 6 hrs after injection in amounts of 6-8 and 0.8 mumol 7-MeG/mol guanine for the high and the low dose, corresponding to a covalent binding index CBI 4-5. The half-life of excretion of 7-MeG was 5 hrs for the high and 15 hrs for the low dose. The extent of methylation at 0-6 of guanine was estimated to be around 0.002-0.01 mumol 0-6 MeG/mol guanine. Data from references concerning methyl methanesulfonate and dimethyl sulfate are compared with those of metrifonate and the genotoxic response of methylating and non-methylating metabolites is discussed.

Induction of somatic mutations but not methylated DNA adducts in lambdalacZ transgenic mice by dichlorvos

In order to examine the in vivo genotoxic activity of dichlorvos, lambdalacZ transgenic mice (Muta Mouse) were treated i.p. with single (4.4 or 11 mg/kg) or multiple (5 x 11 mg/kg) doses of this agent and sacrificed 4 h or 14 days post-treatment for DNA adduct measurement or mutant frequency analysis, respectively. Neither methylated DNA adducts nor an increase in mutant frequency were detected in the bone marrow, white blood cells, liver, spleen, lung, brain and sperm cells after the single doses. However, following multiple dosing a statistically significant 3-fold increase in mutant frequency was observed in the liver, while a non-statistically significant increase was observed in the bone marrow. In contrast, dimethylsulphate, a model methylating agent, gave rise to detectable DNA adducts but no increase in mutant frequency following i.p. administration of single (30 mg/kg) or multiple (10 x 6 mg/kg) doses.

O6-methylguanine and O6-methylguanine-DNA [corrected] methyltransferase activity in tissues of BDF-1 mice treated with antiparasitic drugs

Levels of the DNA promutagenic methylation damage, O6-methylguanine (O6-MeG) and the activity of the O6-methylguanine-DNA methyltransferase (MGMT), the enzyme responsible for repairing O6-MeG, were measured at various time intervals in tissues of BDF-I mice administered a single therapeutic dose of the antischistosomal agents hycanthone, oxaminiquine and metrifonate. Hycanthone increased O6-MeG in the liver-DNA after 6 h, then decreased by 3-fold after 48 h. Lower levels of the adduct and a slower rate of formation were found in the intestine and bladder. MGMT activities were significantly lower in the liver (74%) and bladder (25%) compared to control animals after 6 h, then restored by 48 h. Oxaminiquine increased O6-MeG in all tissues, but spleen, after 6 h and persisted only in the bladder after 48 h. Liver and bladder tissues of these animals exhibited a pattern of alteration in the MGMT activity similar to that observed for hycanthone. Metrifonate induced a profile of O6-MeG comparable to that of oxaminiquine but the levels of the adduct were about 2-fold lower. Hepatic MGMT in these animals was significantly lower (approximately 38%) than the control values after 6 h, then restored by 48 h. A significant negative correlation was obtained between O6-MeG and MGMT activity in the liver (r=- 0.85), intestine (r=- 0.62) and bladder (r=- 0.59). These results demonstrate that treatment with antischistosomal agents may lead to the formation of promutagenic alkylation damage in the tissue DNA and alterations in the DNA repair capacity.

Mammalian toxicology of organophosphorus pesticides

Organophosphorus compounds have been utilized as pesticides for almost five decades. They continue to be used as insecticides, helminthicides, ascaricides, nematocides, and to a lesser degree as fungicides and herbicides. While they have been and continue to be extremely useful in agricultural pest control throughout the world, their extensive use has led to numerous poisonings of nontarget species, including many human fatalities. The primary acute mammalian toxicity associated with exposure to organophosphorus pesticides results from inhibition of the enzyme acetylcholinesterase. However, other toxicities, some of which are life-threatening but not related to acetylcholinesterase inhibition, have been observed following exposure to certain organophosphorus compounds. The focus of the current review is to summarize the known effects, both cholinergic and noncholinergic, of organophosphorus pesticides in mammals. Included in this summary is a discussion of the metabolic activation of organophosphorus pesticides, since this process plays a critical role in mediating the acute toxicities of many of these pesticides.

Investigations of the genotoxicity and cell proliferative activity of dichlorvos in mouse forestomach

This study investigated the possible mechanism by which dichlorvos may have caused forestomach tumours in mice in a chronic corn oil gavage cancer bioassay [NTP (1989) Toxicology and carcinogenesis studies of dichlorvos in F344/N rats and B6C3F1 mice (gavage studies). National Toxicology Program Technical Report 342, NIH Publ. No 89-2598]. For this purpose, a method has been developed to assess the genotoxicity of irritant substances on mouse forestomach epithelium. Groups of five B6C3F1 mice were given a single oral dose of dichlorvos, the genotoxic forestomach carcinogen 1-methyl-3-nitro-1-nitrosoguanidine (MNNG) or the irritant, non-genotoxic forestomach carcinogen butylated hydroxyanisole (BHA). After periods of 2-48 h, three parameters were assessed: unscheduled DNA synthesis (UDS) by autoradiography of tissue sections, replicative DNA synthesis (RDS) also by autoradiography of incorporated [3H]thymidine, and histopathological changes, including hyperplasia. MNNG induced UDS but not RDS or hyperplasia in forestomach epithelium, consistent with its genotoxic mode of action. BHA and dichlorvos did not induce UDS, consistent with absence of genotoxic activity in the forestomach after in vivo exposure. In contrast, BHA and dichlorvos induced RDS and subsequent hyperplasia, which is likely to result from irritant damage. These data suggest that the chronic effects of dichlorvos on mouse forestomach epithelium in the oral gavage bioassay were mediated via enforced cell proliferation, rather than by a genotoxic mechanism.

Formation of promutagenic methylation damage in tissue-DNA of mice treated with antischistosomal agents

The existence of the promutagenic methylation damage O6-MedG has been measured at various time intervals in different tissue DNAs of mice received a single therapeutic dose of various antischistosomal agents (hycanthone, oxaminiquine and metrifonate). Liver-DNA exhibited the highest levels of O6-MedG in all treated animals while, spleen DNA contained the lowest. The three antischistosomal agents tested seemed to exert the peak concentrations of their alkylating metabolites over a period of several hours following the administration. In mice which had received hycanthone, liver-DNA contained readily detectable amounts of O6-MedG by 6 h post-treatment (0.089 mol O6-MedG/mol dG) and by the end of 48 h, this was decreased by about 3-fold to reach a level of 0.026 mumol/mol dG. In intestinal-DNA, however, O6-MedG was formed more slowly and contained about half the level of that found in the liver-DNA. In the tissue-DNA of animals which had received oxaminiquine, the highest level of O6-MedG was observed at 6 h after administration and at a 24-h time point, the adduct dramatically decreased in the liver and intestine-DNA to undetectable values. In neither tissues was there any evidence for O6-MedG accumulation in the DNA at the end of a 48-h post-treatment. A pattern of O6-MedG, almost similar to that of oxaminiquine, was also observed in tissue-DNA of mice pretreated with metrifonate. These results demonstrate that treatment with antischistosomal agents leads to the formation of highly promutagenic alkylated lesions in the tissue-DNA. The implication of such existence for antischistosomal-induced toxicity and carcinogenicity are discussed.

A comparative study of guanine N7-alkylation in mice in vivo by the organophosphorus insecticides trichlorphon, dimethoate, phosmet and bromophos

Following intraperitoneal administration to male mice (strain AB Jena/Halle) of 14C-methyl-labelled trichlorphon, dimethoate, phosmet and bromophos, 10-20 Ci/mol, in dosages of 0.06-0.55 mmol/kg, DNA from liver and kidneys was analyzed for 14C in N-7 methylguanine (7-MeG). The extents of methylation were in the range of 5-10 mumol 7-MeG/mol guanine for trichlorphon and dimethoate and of 0.2-0.4 for phosmet and bromophos, for high doses, respectively Excretion half-lives of 7-MeG were differing between trichlorphon (5 hrs, high dose, and 15-17 hrs, low dose) and dimethoate (23-160 hrs, high dose). The extents of methylation at 0-6 of guanine were estimated to be around 0.01 mumol 0-6 MeG/mol guanine for high doses of organophosphates of sufficient water solubility. Factors associated with the partition of organophosphates in mammalian systems are useful for estimating DNA attack by organophosphates in mammals in vivo.

Activity of organophosphorus insecticides in bacterial tests for mutagenicity and DNA repair--direct alkylation versus metabolic activation and breakdown. II. O,O-dimethyl-O-(1,2-dibromo-2,2-dichloroethyl)-phosphate and two O-ether derivatives of trichlorfon

The following organophosphates were tested for their ability to induce DNA damage in a rec-type repair test with Proteus mirabilis strains PG713 (rec- hcr-) and PG273 (wild-type) and point mutations in the his- strain TA100 of Salmonella typhimurium: O,O-dimethyl-O-(1,2-dibromo-2,2-dichloroethyl)-phosphate (NALED); trichlorfon-O-methyl ether (TCP-O-ME), O,O-dimethyl-(1-methoxy-2,2,2-trichlorethyl)-phosphonate; trichlorfon-O-methyl ether vinyl derivative (TCP-O-MEVD), O,O-dimethyl-(1-methoxy-2,2-dichlorovinyl)-phosphonate. All compounds were negative in the repair test but induced base pair substitutions in S. typhimurium. The mutagenicity of NALED is due to the direct alkylating ability of the parental molecule and to mutagenic metabolites generated by enzymatic splitting of the side chain. Glutathion-dependent enzymes in the S9-mix eliminate the mutagenic activity of NALED completely. Mutation induction by TCP-O-ME and TCP-O-MEVD is predominantly caused by the reactive O-methyl ether configuration of the side chain and is resistant to metabolic inactivation by NADPH- or glutathion-dependent enzymatic pathways in the S9-mix of mice.

Activity of organophosphorus insecticides in bacterial tests for mutagenicity and DNA repair--direct alkylation vs. metabolic activation and breakdown. I. Butonate, vinylbutonate, trichlorfon, dichlorvos, demethyl dichlorvos and demethyl vinylbutonate

The following organophosphates were tested for their ability to induce DNA damage in a rec-type repair test with Proteus mirabilis strains PG713 (rec- hcr-) and PG273 (wild type) and point mutations in his- strain TA100 of Salmonella typhimurium--butonate: O,O-dimethyl-(1-n-butyryloxy-2,2,2-trichloroethyl)-phosphonate; vinylbutonate: O,O-dimethyl-(n-butyryloxy-2,2-dichlorovinyl)-phosphonate; trichlorfon: O,O-dimethyl-(1-hydroxy-2,2,2-trichloroethyl)-phosphonate; dichlorvos: O,O-dimethyl-O-(2,2-dichlorovinyl)-phosphate; the demethylated derivatives--demethyldichlorvos: O-methyl-O-(2,2-dichlorovinyl)-phosphoric acid; demethyl vinylbutonate: O-methyl-(1-n-butyryloxy-2,2-dichlorovinyl)phosphonic acid. Of the six compounds tested, dichlorvos and trichlorfon induced base pair substitutions and DNA damage. No mutagenicity and DNA damage were found in experiments with butonate, vinylbutonate, demethyl vinylbutonate and demethyl dichlorvos. Genotoxic activity for dichlorvos and the absence of both mutagenic and RNA damaging properties for its non-alkylating demethyl derivative favors the hypothesis that alkylation of DNA is the essential step for mutation induction by this organophosphate. Furthermore, the absence of genetic effects after treatment with vinylbutonate and demethyl dichlorvos does not support a crucial role of vinyl or allyl groups in side chains of organophosphates for genetic activity. Microsomal enzymes decreased genetic activity of dichlorvos and trichlorfon in vitro. No evidence for a role of metabolic activation in the mutagenic activity of any of these compounds was found.

Changes in DNA properties due to treatment with the pesticides malathion and DDVP

Properties of calf thymus DNA were investigated after treatment with the pesticides malathion (0,0-dimethyl-S-(1,2-bis ethoxycarbonyl ethyl)dithiophosphate) and DDVP (0,0-dimethyl-0-(2,2 dichlorovinyl)phosphate) in vitro by means of derivative (differential) pulse polarography (DPP), thermal denaturation curves recorded spectrophotometrically (Tm), viscometric measurements, and chromatography on the hydroxyapatite column. Changes in the properties of DNA were observed by means of DPP after only a few hours incubation with the pesticides, whereas the other methods did not detect any changes even after 48 h. The results obtained by DPP indicate that single-stranded segments and thermolabile regions are formed in DNA due to the action of the pesticides. This behaviour could perhaps be a consequence of guanine alkylation followed by depurination and chain scission at elevated temperatures. Malathion and DDVP differ in the kinetics of reaction with double-helical DNA. DDVP is more reactive and its action is also manifested after 72 h in changes in viscosity, Tm, and chromatographic behaviour on the hydroxyapatite column. The changes induced by malathion were, under identical conditions, not detectable by these methods.

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.