Diquat herbicide and rhodamine WT dye were applied in a lake to three
1.6 ha plots either with a polymer, which reportedly aids in sinking a
nd confinement of aquatic herbicides, or without a polymer. Diquat and
dye concentrations were measured at three different depths in the wat
er column within the plots during the first three hours after applicat
ion to determine vertical distribution of diquat and dye, and in compo
site samples at fixed distances from the plot up to 168 hours after ap
plication to determine movement out of the treated plots. Diquat and d
ye were homogeneous in the water column when no polymer was used, but
were concentrated near the surface when polymer was used. This distrib
ution may have resulted from temperature stratification. Polymer did n
ot affect movement of diquat or dye out of the plots. The half-lives o
f diquat within the plots were 25 (SE=6.2) hr, 39 (SE=4.3) hr, and 25
(SE=2.0) hr. Forty-six percent of samples collected at the edges of th
e plots did not contain detectable diquat residues and only 66 percent
of those samples with detectable diquat contained greater than the po
table water tolerance (10 ppb). Diquat was not found in any samples 16
8 hours after application 61 m or farther from the edge of the plots.
Dye and diquat concentrations were weakly correlated within and outsid
e the plots. Dye half-lives were consistently higher than diquat, whic
h suggests that the herbicide was removed from the water by plants and
sediments more rapidly than dye.