Laboratory studies were conducted to determine the mobility of parent pesti
cides and degradation products through the use of large undisturbed soil co
lumns. The influence of vegetation on the mobility of pesticide adjuvants w
as also investigated. Modifications to the laboratory setup of soil columns
for studying various pesticides, degradation products, and adjuvants were
done to fit the needs of the particular compound being studied. To improve
mass balances of volatile parent compounds, such as methyl bromide, as well
as biodegradable (mineralizable) pesticide degradation products such as de
ethylatrazine, modifications of columns to accommodate isolation of volatil
e degradation products were accomplished by enclosure of the column head sp
ace and use of flow-through systems. Evidence of preferential flow of atraz
ine, deethylatrazine, metolachlor, and methyl bromide were indicated by the
presence of either the C-14-compound or Br- (in the case of methyl bromide
-applied soil columns) after the first leaching event. Diffusion through th
e soil matrix was also evident with apeak of C-14 in the leachate several w
eeks after pesticide (or degradate) application to the soil column. Deethyl
atrazine, a major degradate of atrazine, was more mobile than the parent co
mpound. Vegetation had a significant positive effect on reducing the mobili
ty of the adjuvants propylene glycol and ethylene glycol.