The metabolism of herbicide pentoxazone, 3-(4-chloro-5-cyclopentyloxy-2-flu
orophenyl)-5-isopropylidene-1,3-oxazolidine-2,4-dione, was investigated by
soil microorganisms with a liquid medium applied with radiolabeled pentoxaz
one. Four different types of Japanese agricultural soils were inoculated as
the sources of microorganisms. There was no marked difference in the degra
dation profiles among the four soils. Pentoxazone decreased rapidly, and N-
(4-chloro-5-cyclopentyloxy-2-fluorophenyl)-3-methyl-2-oxobutanamide (A-0505
, a hydrolysate at the carbonyl group of C2 in 1,3-oxazolidine-2,4-dione ri
ng followed by decarboxylation) increased up to about 57% of applied dosage
. After transient accumulation of A-0505, N-(4-chloro-5-cyclopentyloxy-2-fl
uorophenyl)-2-hydroxy-3-methylbutanamide (A-1374, a reduction product of A-
0505) increased up to about 71%. The other metabolites, 4-chloro-5-(cyclope
ntyloxy)-2-fluoroaniline aniline (A-0480, an aniline derivative), hydrated-
pentoxazone (another hydrolysate at the carbonyl group of C4 in 1,3-oxazoli
dine-2,4-dione ring) and one unidentified compound were detected over 10% o
f applied dosage. Pentoxazone is likely to be readily transformed by ubiqui
tous soil microorganisms. These microbes which can proliferate in soil/wate
r environment would play an important role in the progress of the degradati
on of pentoxazone.