SOIL METABOLISM OF THE HERBICIDE RIMSULFURON UNDER LABORATORY AND FIELD CONDITIONS

Citation
J. Rouchaud et al., SOIL METABOLISM OF THE HERBICIDE RIMSULFURON UNDER LABORATORY AND FIELD CONDITIONS, Journal of agricultural and food chemistry, 45(8), 1997, pp. 3283-3291
Citations number
20
Categorie Soggetti
Food Science & Tenology",Agriculture,"Chemistry Applied
ISSN journal
00218561
Volume
45
Issue
8
Year of publication
1997
Pages
3283 - 3291
Database
ISI
SICI code
0021-8561(1997)45:8<3283:SMOTHR>2.0.ZU;2-1
Abstract
Procedures were developed for soil analysis of rimsulfuron and its met abolites by means of GC-ECD, GC-FPD and GC-MS with a detection limit o f 1 mu g of rimsulfuron equivalents per kilogram of dry soil, after pu rification of the soil extracts by TLC. Soil containing an exaggerated rimsulfuron concentration was incubated in the laboratory, in order t o adjust the analytical procedures. To evaluate the role of different manuring managements, rimsulfuron was applied postemergence (10 g ha(- 1) on a corn field in 1994 and 1995) on plots treated with (1) green m anure, pig slurry applied in (2) November and (3) March, and cow manur e applied in (4) November and (5) March and (6) untreated control plot s without organic fertilizer. Neither rimsulfuron nor its metabolites were detected at soil depths lower than 8 cm. The results show that ma nure managements prolong rimsulfuron half-life in the 0-8 cm surface s oil layer from a minimum of 14 days (control) to a maximum of 46 days (pig slurry in March). At corn harvest, rimsulfuron and its metabolite s were not detected in soil. Similar soil degradation pathways were ob served in the field as in the laboratory. imidin-2-yl)-N-[3-(ethylsulf onyl)-2-pyridinyl]urea 2 was a transient soil degradation product. ony l)-2-pyridinyl]-4,6-dimethoxy-2-pyrimidineamine 3 attained a maximum s oil concentration after 20 days of incubation and then progressively d isappeared and could not be detected after 40 days. The high-molecular weight amine 3 did not accumulate in soil, eliminating the concern fo r potential formation of nitroso amino compounds. 2-Hydroxy-3-(ethylsu lfonyl)pyridine 4 became the major rimsulfuron soil degradation produc t. The soil concentrations increased and attained a maximum after 40 d ays of incubation and then decreased; its isomerization into 2-pyridon e, followed by hydrolysis, could transform it into low molecular weigh t nontoxic products. The concentrations of 2-amino-4,6-dimethoxypyrimi dine 5 were somewhat lower than those of compound 4.