Insecticide target

Table 3.1 Potential neuronal and muscular insecticide target sites...

Observed differences between strains of rats and mice, as described below, may be the result of gene polymorphisms. In cases involving insecticide selection pressure, resistant populations may arise as a result of direct mutations of insecticide-metabolizing enzymes and/or insecticide target sites that are passed on to succeeding generations. 

Voltage-Gated Sodium Channels as Insecticide Targets... 

Pyrethroid insecticides (deltamethrin, NRDC 157, cismethrin), DDT analogs ( p,j> -DDT, (>,j> -DDT, methoxychlor, EDO), and a DDT-pyrethroid hybrid compound (GH401) enhanced veratridine-dependent sodium uptake by mouse brain synaptosomes The effectiveness of these compounds in the sodium uptake assay was in good agreement with their acute mammalian toxicities. , -DDT also enhanced veratridine-dependent sodium uptake by fish brain synaptosomes These findings demonstrate the utility of ion flux assays to study interactions of insecticides with sodium channels in the central nervous system and to explore species differences in insecticide target site sensitivity ... 

Discovery of the GABA Receptor as an Insecticide Target Site... 

Imidacloprid is a widely used neonicotinoid insecticide that kills pests by targeting their central nAChRs. Levamisol is used to kill nematodes by acting on nAChRs in the worm s muscles. 

Naqvi SM, Vaishnavi C. 1993. Mini Review. Bioaccumulative potential and toxicity of endosulfan insecticide to non-target animals. Comp Biochem Physiol C 105(3) 347-61. 

A striking feature of the toxic compounds considered so far is that many of them are neurotoxic to vertebrates or invertebrates or both. The nervous system of animals appears to be a particularly vulnerable target in chemical warfare. Not altogether surprisingly, all the major types of insecticides that have been commercially successful are also neurotoxins. Indeed, in 2003, neurotoxic insecticides accounted for over 70% of total insecticide sales globally (Nauen 2006). 

The organophosphorons insecticides dimethoate and diazinon are mnch more toxic to insects (e.g., housefly) than they are to the rat or other mammals. A major factor responsible for this is rapid detoxication of the active oxon forms of these insecticides by A-esterases of mammals. Insects in general appear to have no A-esterase activity or, at best, low A-esterase activity (some earlier stndies confnsed A-esterase activity with B-esterase activity) (Walker 1994b). Diazinon also shows marked selectivity between birds and mammals, which has been explained on the gronnds of rapid detoxication by A-esterase in mammals, an activity that is absent from the blood of most species of birds (see Section 23.23). The related OP insecticides pirimiphos methyl and pirimiphos ethyl show similar selectivity between birds and mammals. Pyrethroid insecticides are highly selective between insects and mammals, and this has been attributed to faster metabolic detoxication by mammals and greater sensitivity of target (Na+ channel) in insects. 

Resistance to DDT has been developed in many insect species. Although there are some cases of metabolic resistance (e.g., strains high in DDT dehydrochlorinase activity), particular interest has been focused on kdr and super kdr mechanisms based upon aberrant forms of the sodium channel—the principal target for DDT. There are many examples of insects developing resistance to dieldrin. The best-known mechanism is the production of mutant forms of the target site (GABA receptor), which are insensitive to the insecticide. 

Gamma aminobutyric acid (GABA) receptors are located on the postsynaptic membranes of inhibitory synapses of both vertebrates and insects and contain within their membrane-spanning structure a chloride ion channel. They are found in both vertebrate brains and invertebrate cerebral ganglia (sometimes referred to as brains) as well as in insect muscles. Particular attention has been given to one form of this receptor—the GABA-A receptor—as a target for novel insecticides (Eldefrawi and Eldefrawi 1990). It is found both in insect muscle and vertebrate brain. The remainder of this description will be restricted to this form. 

Salgado, V.L. (1999). Resistant target sites and insecticide discovery. In G.T. Brooks and T.R. Roberts (Eds.) Pesticide Chemistry and Bioscience—The Food-Environment Challenge. Cambridge, Royal Society of Chemistry 236-246. 

Von Keyserlingk, H.C. and Willis, R.J. (1992). The GABA-activated CL channel in insects as a target for insecticide action—a physiological study. In D. Otto and B. Weber (Eds.) Insecticides Mechanism of Action and Resistance. Andover, U.K. Intercept. 

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