One explanation for unexpectedly widespread ground water contamination from
atrazine (2-chloro-4-ethylamino-6-isopropylamino-s-triazine) may be the oc
currence of colloid-facilitated transport, whereby the dissolved herbicide
becomes adsorbed to mobile colloids that migrate through preferential now-p
aths in the soil zone and into the ground water. The objectives of this stu
dy were to determine the extent of adsorption of atrazine to bulk soil and
to soil colloids and to determine the extent of colloid-facilitated transpo
rt of atrazine at a field site in Virginia during simulated rainfall events
. Equilibrium batch adsorption experiments were performed over a concentrat
ion range of 0.05 to 10.0 mg atrazine L-1 on bulk soil samples and on collo
idal suspensions of 75 mg L-1, a concentration comparable with those observ
ed at the field site. Linear partition coefficients ranged from 0.496 to 2.
48 L kg(-1) for the bulk soil and from 70.8 to 832 L kg(-1) for the soil co
lloids. In the field, gravity lysimeters were installed at a depth of 25 cm
below the surface of six 0.25-m(2) undisturbed plots. Mass recovery of sur
face-applied atrazine in the lysimeters was not significantly affected by r
ainfall rate and was, on average, 2.7% for plots receiving 25 mm h(-1) simu
lated rainfall and 3.6% for plots receiving 50 mm h(-1) simulated rainfall.
Of the total atrazine collected in the Lysimeters, the fraction that was c
olloid-associated ranged from 4.9 to 30% (mean of 15%), indicating that a m
easurable portion of mobile atrazine is transported via association with co
lloids.