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Influence of straw management, nitrogen fertilization and dosage rates on the dissipation of five sulfonylureas in soil
Author(s) -
Menne H J,
Berger B M
Publication year - 2001
Publication title -
weed research
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.693
H-Index - 74
eISSN - 1365-3180
pISSN - 0043-1737
DOI - 10.1046/j.1365-3180.2001.00234.x
Subject(s) - straw , chemistry , nitrogen , fertilizer , nitrogen fertilizer , agronomy , zoology , human fertilization , field experiment , horticulture , biology , inorganic chemistry , organic chemistry
The dissipation behaviour of metsulfuron‐methyl, tribenuron‐methyl, thifensulfuron‐methyl, triasulfuron and amidosulfuron were studied in soil following post‐emergence spring applications to cereal crops. Incorporation or removal of straw and different fertilizer applications had no influence on the disappearance time (DT 50 ) of the herbicides. However, in laboratory trials dissipation of metsulfuron‐methyl, triasulfuron and amidosulfuron at higher application rates was accelerated after incorporation of straw into the soil. The addition of straw decreases soil pH thereby causing faster hydrolysis of the compounds. Addition of nitrogen fertilizer increased the half‐lives (t 1/2 ) of the herbicides. Combination of both straw and N fertilizer, however, had no effect. Neither straw nor N influenced the degradation of tribenuron‐methyl and thifensulfuron‐methyl. The DT 50 of all herbicides investigated varied from 6 to 17 days in the field trials. Except for amidosulfuron, herbicides could not be detected 38–68 days after application. In the laboratory, t 1/2 values were higher than those in the field at 75 days (amidosulfuron), 63 days (metsulfuron‐methyl), 35 days (triasulfuron) and 13 days (tribenuron‐methyl). Only the t 1/2 of thifensulfuron‐methyl was at 29 h faster under laboratory conditions. T 1/2 values of all herbicides were influenced by their initial concentration. The t 1/2 values of amidosulfuron and tribenuron‐methyl at 1 mg a.i. kg −1 soil were 2–2.5 times higher than at the recommended field application rate of 42 μg a.i. kg −1 soil.