The herbicide metamitron 4-amino-3-methyl-6-phenyl-1,2,4-triazin-5(4H)
-one) photodegrades rapidly in aqueous solution leading to the formati
on of desaminometamitron. Photolysis rate was slower in the presence o
f soils due to the screen effect of soil particles, although some diff
erences observed between the 3 different soils indicated that soil org
anic matter (SOM) may accelerate photolysis of metamitron. Photolysis
studies with the colloidal fraction of the soils before and after orga
nic matter elimination and with soil humic acids confirmed the photose
nsitizing effect of humic acid on the phototransformation of metamitro
n. Studies with model iron oxides (goethite and ferrihydrite) also sug
gested that these soil components could accelerate metamitron degradat
ion in aqueous medium. The Fe2O3-sensitizing effect is less significan
t than that of the SOM and was not clearly developed in the natural cl
ay fraction. Copyright (C) 1996 Elsevier Science Ltd