The fate of pesticides in aquifers is influenced by the small but not insig
nificant adsorption of pesticides to mineral surfaces. Batch experiments wi
th five pesticides and four minerals were conducted to quantify the contrib
utions to adsorption from different mineral surfaces and compare adsorption
characteristics of selected pesticides. Investigated mineral phases includ
ed quartz, calcite, kaolinite, and alpha -alumina. Selected pesticides comp
rised atrazine (6-chloro-N-2-ethyl-N-4-isopropyl-1,3,5-triazine-2,4-diamine
isoproturon [3-(4-isopropyl-phenyl)-1,1-dimethylurea)], mecoprop [(RS)-2-(
4-chloro-2-methyl phenoxy)propionic acid], 2,4-D (2,4-dichlorophenoxyacetic
acid), and bentazone [3-isopropyl-1H-2,1,3-benzothiadiazin-4-(3H)-one 2,2-
dioxide]. Specific surface area and mineral surface charge proved to be imp
ortant for the adsorption of these pesticides. Detectable adsorption of the
anionic pesticides (mecoprop, 2,4-D, and bentazone) was only measured when
positive sites were present on the mineral surface. However, when CaCl2 wa
s added as an electrolyte, a detect able adsorption of mecoprop and 2,4-D w
as also measured on kaolinite (which exhibits a negative surface charge), p
robably due to formation of Ca-pesticide-surface complexes. Adsorption of t
he uncharged pesticides (atrazine and isoproturon) was detected only on kao
linite. The lack of adsorption on alpha -alumina indicates that the uncharg
ed pesticides have a greater affinity for the silanol surface sites (= SiOH
) than for the aluminol surface sites (= AIOH) in kaolinite. No measurable
effect of ionic strength was found for the uncharged pesticides. The result
s indicate that quartz and calcite play a smaller role than clay minerals.