Sr. Sorensen et J. Aamand, Biodegradation of the phenylurea herbicide isoproturon and its metabolitesin agricultural soils, BIODEGRADAT, 12(1), 2001, pp. 69-77
Degradation of the phenylurea herbicide isoproturon (3-(4-isopropylphenyl)-
1,1-dimethylurea) and several phenylurea and aniline metabolites was studie
d in agricultural soils previously exposed to isoproturon. The potential fo
r degradation of the demethylated metabolite 3-(4-isopropylphenyl)-1-methyl
urea in the soils was much higher compared to isoproturon. In the most acti
ve soil only 6% of added C-14-labelled isoproturon was mineralised to C-14(
2) within 20 days while in the same period 45% of added C-14-labelled 3-(4-
isopropylphenyl)-1-methylurea was mineralized. This indicates that the init
ial N-demethylation may be a limiting step in the complete mineralization o
f isoproturon. Repeated addition of 3-(4-isopropylphenyl)-1-methylurea to t
he soil and further subculturing in mineral medium led to a highly enriched
mixed bacterial culture with the ability to mineralize 3-(4-isopropylpheny
l)-1-methylurea. The culture did not degrade either isoproturon or the dide
methylated metabolite 3-(4-isopropylphenyl)-urea when provided as sole sour
ce of carbon and energy. The metabolite 4-isopropyl-aniline was also degrad
ed and utilised for growth, thus indicating that 3-(4-isopropylphenyl)-1-me
thylurea is degraded by an initial cleavage of the methylurea-group followe
d by mineralization of the phenyl-moiety. Several attempts were made to iso
late pure bacterial cultures degrading 3-(4-isopropylphenyl)-1-methylurea o
r 4-isopropyl-aniline, but they were not successful.