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A 76-year old farmer ingested 100 g of chlorphenamidine (Galectron), a plant acaricle, for the purpose of suicide. Gastric lavage was performed and the patient survived. Methemoglobinemia was noted after emergency treatment and was still present at 20 hours after ingestion of the compound. The patient was lethargic for at least 50 hours. Moderate neutrophilic leukocytosis and kidney injury were observed.
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The aim of this work was to learn the toxicity of acaricides: monocrotophos, chlorobenzilate and chlorphenamidine when used as an immersion and as a spray on the phytophagous mites, Tetranychus (T) urticae, Tetranychus (T) cinnabarinus and Tetranychus (T) ludeni under laboratory conditions. It was concluded that the mite T. urticae was sensitive to chlorphenamidine at least when used as a spray without killing them in a significant level. However the mites T. cinnabarinus and T. ludeni were sensitive to chlorphenamidine when using immersion method. The monocrotophos and the chlorobenzilate were toxic of the three species of mites using though the employed methods.
An outbreak of hematuria occurred from May 20 to May 23, 1975, among employees of a chemical packaging plant. Nine of 22 workers who packaged the insecticide chlordimeform in a separate shed became severely ill with abdominal pain, dysuria, urgency to void, or hematuria. None of 18 persons who worked in other areas of the plant were affected. Four additional workers who had packaged the chemical during the previous year had a history of similar symptoms. Bladder biopsy specimens from three affected persons showed severe hemorrhagic cystitis; chlordimeform and 2-methyl-4-chloroaniline, a metabolite of chlordimeform, were present in urine specimens collected three days after exposure. The illness lasted from one week to two months; the workers recovered completely. Chlordimeform that was injected subcutaneously into three cats produced similar, though less severe, changes in the bladders of two animals.
The information available concerning the effects of compounds utilized as pesticides on functions of the reticuloendothelial system is quite limited. Review of selected examples of such studies in this and other reports (3) reveals considerable diversity in terms of species of experimental animal, purity and dose of pesticide, length of exposure, and class of pesticide employed. Observations include depression, enhancement, or no significant effect on the selected reticuloendothelial system function studies. With the present available information it is difficult to formulate general conclusions or to predict whether or not any individual pesticide will consistently and significantly alter any specific function of the reticuloendothelial system. At the present time, it is not known if pesticides within a single chemical class act in a similar manner in regard to their ability to influence reticuloendothelial system function. In addition, the relationship, if any, between the toxic, mutagenic teratogenic, or carcinogenic potential of any pesticide and its ability to alter the reticuloendothelial system is also unknown. More extensive systematic studies in experimental animal models would appear to be required before protocols to effectively evaluate the potential of pesticides to influence reticuloendothelial system function in man can be developed.
Chlordimeform (N'(4-chloro-o-tolyl)-N, N-dimethylformamidine; CDM) is a formamidine insecticide acaricide whose major active metabolite is its N-monomethyl analog, desmethylchlordimeform, (DCDM). While their pesticidal action in invertebrates appears to be related to activation of octopamine receptors, their mechanism of action in mammals has not been established. Because of similarities between octopamine and adrenergic receptors and suggestions of CDM and DCDM action on adrenoceptors, the in vitro interactions of CDM and DCDM with adrenoceptors were studied. In mouse brain membrane preparations CDM inhibited the binding of [3H]-clonidine to alpha 2- adrenoceptors and of [3H]-WB4101 to alpha 1-adrenoceptors with IC50 values of 18.2 and 87 microM, respectively. DCDM was a much more potent inhibitor, with IC50 values toward alpha 2-, and alpha 1-adrenoceptors of 44 nM and 1 microM, respectively. Both compounds were only weak inhibitors of the binding of [3H]-dihydroalprenolol to beta-adrenoceptors and of [3H]-quinuclidinyl benzilate to muscarinic receptors and were inactive toward benzodiazepines and gamma aminobutyric acid (GABAA) receptors. Inhibition of [3H]-clonidine binding by both compounds was competitive, as indicated by a decreased receptor affinity without changes in receptor density. Interaction of CDM and DCDM with [3H]-WB4101 binding, on the other hand, was more complex, and not of the competitive type. These results show that CDM and its metabolite DCDM can interact directly in vitro with alpha-adrenergic receptors, suggesting that these receptors could mediate some of the effects of CDM and DCDM in vivo.
Low doses of the formamidine pesticide, chlordimeform (CDM) induce voracious daytime feeding in non-food deprived rats. Following CDM (10 mg/kg), food intakes were five times control intakes after 3 h and 1.1 times control intakes after 24 h. Other selected formamidines, such as the N-demethylated metabolite of CDM, and amitraz, increased 3-h food intake by two and five times control intake, respectively. Anorexia accompanied by excessive CNS stimulation was noted with higher doses of CDM (above 40 mg/kg) and other formamidines. This contrasts with the sedation usually observed with high doses of other structurally diverse appetite stimulants. In addition, hyperphagia was not observed with other CNS stimulants or local anesthetics such as amphetamine, cocaine, and holocaine. Thus the formamidines constitute a new class of appetite stimulants, which should prove to be useful agents for the study of feeding behavior.
The formamidine pesticides amitraz and chlordimeform have recently been shown to be potent proconvulsants (Gilbert 1988). Two main neuroactive properties have been identified as mediators of formamidine neurotoxicity, alpha-2 adrenergic agonism and local anesthetic actions. These two proposed mechanisms of formamidine action were contrasted using electrical kindling of the amygdala. Male rats were administered 0, 10 and 40 mg/kg of the local anesthetic lidocaine, 0, 0.01 and 0.10 mg/kg of the alpha-2 adrenergic agonist clonidine or 0, 10 and 30 mg/kg chlordimeform, IP, once per day. After each injection, kindling stimulation was delivered through chronically-implanted electrodes. The high dosage of chlordimeform and both dosages of lidocaine enhanced the rate of kindling development (mean sessions to stage 5 seizures = 8.6 +/- 1.16, 10.15 +/- 1.04 and 8.5 +/- 0.95, respectively) relative to controls (mean = 14.59 +/- 1.36). Afterdischarge (AD) durations were increased over the first seven sessions by both treatments, but the total cumulative AD did not differ from controls. Clonidine, by contrast, delayed kindling development (mean 27.57 +/- 1.97) and shortened the mean AD duration over the first seven sessions. These data provide support for a local anesthetic action of chlordimeform and stand in contrast to several recent demonstrations of alpha-2 activity of formamidines as a primary contributor to formamidine toxicity.
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The uptake and persistence of 14C-labeled pesticides in cultur-s of human embryonic lung diploid cells were studied. Chlordimeform, DDT, parathion, aldrin and dieldrin were selected as test compounds. Results obtained from these experiments divided the chemical into two groups. The first group consisted of three chemical DDT, aldrin and dieldrin which are generally classified as persistent insecticides while the second group was composed of chlordimeform and parathion, generally considered to be non-persistent insecticides. The rate of initial cellular incorporation of first group was approximately 20 to 70 times greater than the non-persistent insecticides. During the course of an incubation, the amounts of pesticide taken up by the cells decreased gradually.
Inhibition constants of several formamidines, their corresponding formanilides and other representatives of compounds derived from aniline, such as phenylureas, N-phenyl-carbamates and acylanilides, were determined for rat liver monoamine oxidase. The reversability of the inhibition and the lack of correlation between inhibition potencies and toxicities of the compounds tested add to the opinion that MAO inhibition is not a prominent factor in chlordimeform poisoning.
Brain homogenates of Locusta migratoria are found to possess enzyme capable of catalyzing the N-acetylation of tryptamine. A main product of the enzymatic reaction is isolated and identified as N-acetyltryptamine by chromatography analyse. Both insecticides, chlordimeform and lindane, inhibit enzyme activity. A direct correlation between the degree of intoxication and acetylation of tryptamine is described.
The action of the acaricide, chlorodimeform and its metabolite. N-desmethylchlorodimeform, on the activity monoamine oxidase (MAO) from the cattle tick, Boophilus microplus, were studied. Both compounds were found to be potent in vitro and in vivo inhibitors of the enzyme. However the inhibition of MAO does not seem to be related to the toxic action of the acaricide.