Biochemical mechanisms contributing to species differences in insecticidal toxicity

Comparison of published LD(50) or LC(50) levels for a variety of insecticides in several vertebrate species indicate that a wide range of toxicity levels exist, and these cannot be easily predicted within either a chemical group or within a species. There is a relatively limited data base documenting interactions between insecticides and other chemicals, either agricultural or non-agricultural; however, the fact that all major insecticide groups perturb nervous system function as their primary mechanism of acute toxicity suggests the potential for interactions. Studies in our laboratories on a select group of phosphorothionate insecticides in rats indicated that brain acetylcholinesterase sensitivity to inhibition by the oxons, the active metabolites of the phosphorothionates, does not correlate with acute toxicity levels. The activities and properties of hepatic cytochrome P450-mediated activation (desulfuration) and detoxication (dearylation) of the phosphorothionates as well as of A-esterase-mediated hydrolysis of oxons contribute substantially to understanding the acute toxicity levels in rats, as does the sensitivity of the protective aliesterases to phosphorylation. However, in the channel catfish, the acetylcholinesterase sensitivity to oxon inhibition reflects the acute toxicity level of these same insecticides, and may be largely responsible for determining the acute toxicity level in this species. Thus, metabolism of insecticides appears to be far more influential in some species than others in determining the toxicity elicited.