Cyclic voltammetry and controlled-potential (bulk) electrolysis have been employed to investigate the electrochemical reduction of 4,4 -(2,2,2-trichloroethane-1,1-diyl)bis(methoxybenzene), commonly known as the pesticide methoxychlor, at glassy carbon and silver cathodes in dimethylformamide (DMF) containing 0.050 M tetra-n-butylammonium tetrafluoroborate (TBABF 4 ). Reduction of methoxychlor at both glassy carbon and silver shows four voltammetric peaks, the first three of which are associated with cleavage of carbon-chlorine bonds; the fourth peak is assigned to reduction of 4,4 -(ethene-1,1-diyl)bis(methoxybenzene). Bulk electrolyses of methoxychlor at reticulated vitreous carbon and silver mesh cathodes at potentials corresponding to each of the first three voltammetric peaks were conducted; coulometric n values and product distributions (determined by means of GC and GC-MS techniques) depend on potential. In particular, two completely dechlorinated products, namely 4,4 -(ethane-1,1-diyl)bis(methoxybenzene) and 4,4 -(ethene-1,1-diyl)bis(methoxybenzene) have been identified and quantitated. A mechanistic scheme is proposed to account for the formation of the various products. When global use of the infamous pesticide 4,4 -(2,2,2-trichloroethane-1,1-diyl)bis(chlorobenzene) (1)-known more familiarly as DDT-was restricted, a close relative, namely 4,4 -(2,2,2-trichloroethane-1,1-diyl)bis(methoxybenzene) (2) or methoxychlor, became a temporarily popular replacement. Unfortunately, when concerns about the toxicity of 2 arose, it was banned in the European Union in 2002 and became unregistered in the United States in 2003. However, in other parts of the world, 2 is still employed as an agricultural pesticide and for home applications in the treatment of flea and fly infestations.Like many members of the family of halogenated pesticides, methoxychlor degrades very slowly in the environment, which allows for its transport and subsequent detection in Arctic samples far from the original point of use.1 For hydrolytic degradation pathways in aquatic systems of pH 6-9, the half-life is approximately one year, and the resulting olefinic metabolite degrades even more slowly.2 When exposed to sunlight, this olefin derivative undergoes an interesting photoisomerization in water.3 Sunlight increases the photolysis rate, so that the half-life at the surface of distilled water is closer to 4.5 months, and even faster in natural waters where half-lives of only 2-5 h are seen. 4 Biological degradation of methoxychlor results in the loss of one chlorine as well as demethylation of the hydroxylbenzene moieties.5 Uptake of methoxychlor in a model ecosystem has also been examined; whereas methoxychlor was found to be in a dynamic state in fish, it accumulated in snails. Furthermore, incubated mouse livers were unable to metabolize methoxychlor and 97% was recovered. 6 Concerns about the accumulation of methoxychlor in humans prompted studies conducted in the agricultural region of Spain * Electrochemical Society Student Member. * * E...