Patterns of epoxide metabolism by epoxide hydrolase and glutathione S-transferase associated with age and genotype in Drosophila melanogaster

Adaptive relationships of epoxide hydrolase in herbivorous arthropods

Epoxide hydrolase catalyzes a simple hydrolysis of reactive cyclic ethers that may otherwise alkylate and impair critical proteins and nucleic acids required for life. Although much less studied than the cytochrome P-450 monooxygenases that produce epoxides, differences in subcellular, tissue, pH, substrate, and inhibitor specificities argue for at least three forms of insect epoxide hydrolase. Increasing numbers of epoxides are being identified as plant allelochemicals, antifeedants, and essential hormones or precursors for herbivorous arthropods, and in many cases an associated alkene to diol pathway of metabolism is found. A role for epoxide hydrolase in arthropod-plant interactions is strongly supported by species comparisons and by age-activity and induction studies. Two major limitations for study in biochemical ecology of epoxide hydrolase are the lack of an effective in vivo inhibitor and a range of commercially available radiolabeled substrates for the enzymes.

Characterization and cDNA cloning of a clofibrate-inducible microsomal epoxide hydrolase in Drosophila melanogaster

In order to understand the roles of the epoxide hydrolases (EHs) in xenobiotic biotransformation in insects, we examined the induction of EHs by exogenous compounds in Drosophila melanogaster third instar larvae. Among the chemicals tested, clofibrate, a phenoxyacetate hypolipidermics drug, increased EH activity towards cis-stilbene oxide approximately twofold in larval whole-body homogenates. The same dose of clofibrate also induced glutathione S-transferase activity. The effect of clofibrate on EH induction was dose-dependent and the highest activity occurred with a 10% clofibrate application. Three other substrates conventionally used in EH assays (trans-stilbene oxide, trans-diphenylpropene oxide and juvenile hormone III) were poorly hydrolysed by larval homogenates, with or without clofibrate administration. Because the increased EH activity was localized predominantly in the microsomal fraction, we synthesized degenerate oligonucleotide primers with sequences corresponding to conserved regions of known microsome EHs from mammals and insects in order to isolate the gene. The 1597 bp putative cDNA of D. melanogaster microsomal EH (DmEH) obtained from a larval cDNA library encoded 463 amino acids in an open reading frame. Northern blot analysis showed that the transcription of DmEH was increased in larvae within 5 h of clofibrate treatment. Recombinant DmEH expressed in baculovirus hydrolysed cis-stilbene oxide (23 nmol.min-1.mg protein-1) and was located mainly in the microsomal fraction of virus-infected Sf9 cells. There was no detectable EH activity toward juvenile hormone III. These observations suggest that DmEH is involved in xenobiotic biotransformation, but not in juvenile hormone metabolism, in D. melanogaster.

Genotoxicity and carcinogenicity testing of 1,2-dibromopropane and 1,1,3-tribromopropane in comparison to 1,2-dibromo-3-chloropropane

The activities of 1,2-dibromopropane (DBP) and 1,1,3-tribromopropane (TBP) were studied in seven genotoxicity assays, (i) SOS-induction in E. coli, (ii) DNA repair in primary rat hepatocyte culture, (iii) the Salmonella/microsome assay, (iv) a host-mediated assay using Salmonella, (v) the somatic mutation and recombination assay in Drosophila melanogaster, (vi) HGPRT-mutagenesis assay in ARL 18 cells, and (vii) micronucleus formation assay in mouse polychromatophylic erythrocytes (PCE), forestomach (FS), glandular stomach (GS), duodenum (D), jejunum (J), cecum (C) and liver (L). The halopropanes were also tested for tumor formation in the fish Danio rerio. DBP was active in assays (ii), (v), (vii FS) and (vii L). TBP was positive in assays (ii) and (iii), strongly positive in (vii L) and borderline positive in (iv). However, neither DBP nor TBP induced tumors in fish, in contrast to the carcinogenic 1,2-dibromo-3-chloropropane. The genotoxicity and potential carcinogenicity of DBP and TBP in mammals is discussed.

Anionic glutathione S-transferases in shrimp eyes

1. Two anionic isoenzymes of glutathione transferases (EC 2.5.1.18), QI and QII, have been purified from the eyes of the shrimp Penaeus japonicus by using a combination of S-hexylglutathione affinity column chromatography and Mono-Q fast protein liquid chromatography (f.p.l.c.). 2. Both QI and II glutathione S-transferases are homodimers. They show similarity in substrate specificities and pH optima, but not in isoelectric points. 3. QI is distinct from QII by anion-exchange f.p.l.c., reverse-phase h.p.l.c. chromatography and amino acid sequencing analysis. QI has N-terminal amino acid sequences homologous to mu glutathione S-transferase, whereas QII is homologous to theta glutathione S-transferases.