The effects of water percolating through [rmg-MC] carbofuran-treated soils (3.6 ppm; 2.9 gCi) and of the fungicide captafol and the herbicide EPTC on the persistence, movement, and metabolism of the insecticide in an agromicrocosm were investigated. After a 3-week incubation period, 49% of the soil-applied radiocarbon had been removed with percolating water from soils, while 37 % was recovered from soils and corn. In nonpercolated soils, however, 80% of the applied 14C was still associated with soils and corn. The aquatic components (water, lake mud, Elodea plants, and guppy fish) contained 25% of the soil-applied radioacrbon at the end of the experiment, even though 49% had been initially added to the aquariums via the percolated water. This loss of 24% was partially accounted for by degradation of 14C-labeled compounds to 14C02. About a/4 of all the radiocarbon found in the aquatic system was associated with the lake bottom mud, most of it as unextractable 14C-labeled compounds. Carbofuran was the major compound recovered from control and percolated soils, amounting to 39% and 15% of applied radiocarbon, respectively, while 3-ketocarbofuran and 3-hydroxycarbofuran were identified as the major metabolites. The aquatic component, however, contained only 0.3% of the initially applied [14C]carbofiiran, and most of this was associated with the bottom mud layer. While the addition of captafol to [14C]carbofuran-treated soils resulted in a more rapid disappearance of the insecticide from terrestrial soils and a reduced uptake of 14C-labeled compounds by com plants, EPTC had no effects. In the aquatic components, however, captafol and EPTC caused increased recoveries of 14C-labeled residues from lake bottom mud.