Toxicity-metabolism relationship of the photoisomers of certain chlorinated cyclodiene insecticide chemicals.

Abstract

Photoaldrin, photodieldrin, and photoheptachlor are more toxic than their corresponding parent compounds (aldrin, dieldrin, and heptachlor) to freshwater invertebrates and vertebrates, and to adult houseflies. The increase in toxicity is very significant in the case of the amphipod,Gammarus (1.5–12 times), bluegill fry (3.6–5.7 times), mosquito larvae,Aedas (2.3–6 times), minnow fry (2.5 times), and the isopid,Asellus (2 times). The greatest increases occur with photodieldrin which is 12 and 5 times more toxic than dieldrin, respectively, toGammarus, and to blue-gill fry, and with photoaldrin which is 6 and 4 times more toxic than aldrin, respectively, to mosquito larvae and bluegill fry. The toxicities of the photoisomers of isodrin and chlordene are generally less than those of their parent compounds to all the organisms tested. The basis of the differences in toxicities of the chlorinated cyclodiene photoisomers appears to be related to their chemical structure which possibly affects their action at the site(s) of toxic action and/or detoxication. The acidic proton present at the secondary chloride in photoaldrin, photodieldrin, and photoheptachlor possibly is responsible for the formation of charge-transfer complexes between components of the nerve and the mixed-function oxidase; the latter enzyme apparently dehydrochlorinates these photo products to their corresponding, more toxic ketones. The absence of such protons in photoisodrin and photochlordene renders them incapable of forming such ketones. The inhibition of these reactions by sesamex in house flies increases the stability of the chlorinated cyclodiene insecticides and, thus, significantly affects their toxicity. The conversion of photoaldrin, photodieldrin, and photoheptachlor to more-toxic and lipophilic ketones warrants additional studies of their accumulation and subsequent concentration by the food chain.