This study examined the dissipation and carry-over of quinclorac residues i
n a Lethbridge sandy clay loam with 2% organic matter. Experiments were con
ducted in covered outdoor lysimeters using different simulated rainfall reg
imes. Quinclorac residues were monitored in the: top 10 cm of soil using ch
emical residue analysis and the activity of carried-over residues assessed
by bioassay. Quinclorac dissipation was very slow although, in general, the
amount of residue remaining decreased with increased moisture (117-447 mm)
applied. Forty-eight weeks after quinclorac application, 85, 66, 52, 49, a
nd 48% of initial residues remained in the very dry, dry, normal, wet and v
ery wet moisture regimes, respectively. Residue persistence could be accura
tely predicted (r(2) = 0.96) using a simple moisture model (% quinclorac re
maining = 101% - 0.18 x mm cumulative moisture) for up to 300 mm moisture.
Quinclorac dissipation was attributed mostly to the residues leaching beyon
d the 0- to IO-cm soil layer. A separate laboratory experiment showed that
80% of applied quinclorac leached through 9.7-cm deep soil columns when 304
mm of water was applied. The quinclorac residues remaining after 48 wk wer
e biologically available and caused injury to fababeans (Vicia faba L.) und
er all moisture regimes.