“…However, toxaphene residues are still detected in food samples as well as in environmental samples all around the world. − High toxaphene levels were determined in marine organisms, especially in fatty fish and marine mammals. For example, Vetter et al reported 5–1460 μg/kg wet weight of CTTs in different seal species, which was a higher level than hexachlorocyclohexane (4–660 μg/kg) and hexachlorobenzene (0.2–230 μg/kg) detected in the same samples. − However, the toxaphene residue pattern in these higher organisms differed vastly from the complexity of the technical product. , One octa- and one nonachlorobornane, 2- exo ,3- endo ,5- exo ,6- endo ,8,8,10,10-octachlorobornane (B8-1413) and 2- exo ,3- endo ,5- exo ,6- endo ,8,8,9,10,10-nonachlorobornane (B9-1679), were found to be particularly recalcitrant in marine mammals. , Transformation of the many hundred less persistent CTTs may occur abiotically by UV light. , Comparatively little is currently known about the mechanisms of biotic transformation of toxaphene. − Next to reductive dechlorination, , hydroxylation via the phase-I reaction of the detoxification metabolism represents one plausible degradation pathway, which has already been shown for similar xenobiotics . Chandurkar and Matsumura verified the formation of five hydroxylated metabolites by enzymatic transformation of toxaphene in rat livers under laboratory conditions. , Furthermore, in vitro experiments with toxaphene-spiked microsomes of marine mammals, e.g., sperm whales ( Physeter macrocephalus ) and harbor seals ( Phoca vitulina ), resulted in toxaphene transformation along with the tentative detection of one mono- and one trihydroxylated metabolite formed after incubation with NADPH .…”