Degradation in soil and water and ecotoxicity of rimsulfuron and its metabolites

The degradation and ecotoxicity of sulfonylurea herbicide rimsulfuron and its major metabolites were examined in batch samples of an alluvial sandy loam and in freshwater. An HPLC–DAD method was adapted to simultaneously identify and quantify rimsulfuron and its metabolites, which was successfully v...

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Veröffentlicht in:Chemosphere (Oxford) 2001-11, Vol.45 (4), p.515-522
Hauptverfasser: Martins, Jean M.F., Chevre, Nathalie, Spack, Lionel, Tarradellas, Joseph, Mermoud, André
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container_start_page 515
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creator Martins, Jean M.F.
Chevre, Nathalie
Spack, Lionel
Tarradellas, Joseph
Mermoud, André
description The degradation and ecotoxicity of sulfonylurea herbicide rimsulfuron and its major metabolites were examined in batch samples of an alluvial sandy loam and in freshwater. An HPLC–DAD method was adapted to simultaneously identify and quantify rimsulfuron and its metabolites, which was successfully validated by GC–MS analysis. In aqueous solutions, pure rimsulfuron was rapidly hydrolyzed into metabolite 1 ( N-(4,6-dimethoxypyrimidin-2-yl)- N-(3-(ethylsulfonyl)-2-pyridinylurea)), which itself was transformed into the more stable metabolite 2 ( N-((3-(ethylsulfonyl)-2-pyridinyl)-4,6-dimethoxy-2-pyrimidineamine)), with half-life ( t 1/2) values of 2 and 2.5 days, respectively. Hydrolysis was instantaneous under alkaline conditions (pH = 10). In aqueous suspensions of the alluvial soil (pH = 8), formulated rimsulfuron had a half-life of 7 days, whereas that of metabolite 1 was similar to that in water (about 3.5 days). The degradation of the two major metabolites was also studied in soil suspensions with the pure compounds at concentrations ranging from 1 to 10 mg l −1 . The half-life of metabolite 1 ranged from 3.9 to 5 days, close to the previous values. Metabolite 2 was more persistent and its degradation is strongly dependent on the initial concentration ( C 0): half-life values ranged from 8.1 to 55 days at 2–10 mg l −1 , respectively. These values are higher than those determined from the kinetics of metabolite 1 transformation into metabolite 2 ( t 1/2=8–19 days). The ecotoxicity of the three chemicals was evaluated through their effect on Daphnia magna and Vibrio fischeri (Microtox ® bioassay). No effect was observed on D. magna with 24 and 48 h acute toxicity tests. Similarly, no toxic effect was observed with the Microtox ® test for the three chemicals in the range of concentrations tested that included the field application dose. Thus, being of low persistence and lacking acute toxicity, these chemicals present a low environmental risk. However, chronic effects should be studied in order to confirm the safety of rimsulfuron and its major metabolites.
doi_str_mv 10.1016/S0045-6535(01)00040-6
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An HPLC–DAD method was adapted to simultaneously identify and quantify rimsulfuron and its metabolites, which was successfully validated by GC–MS analysis. In aqueous solutions, pure rimsulfuron was rapidly hydrolyzed into metabolite 1 ( N-(4,6-dimethoxypyrimidin-2-yl)- N-(3-(ethylsulfonyl)-2-pyridinylurea)), which itself was transformed into the more stable metabolite 2 ( N-((3-(ethylsulfonyl)-2-pyridinyl)-4,6-dimethoxy-2-pyrimidineamine)), with half-life ( t 1/2) values of 2 and 2.5 days, respectively. Hydrolysis was instantaneous under alkaline conditions (pH = 10). In aqueous suspensions of the alluvial soil (pH = 8), formulated rimsulfuron had a half-life of 7 days, whereas that of metabolite 1 was similar to that in water (about 3.5 days). The degradation of the two major metabolites was also studied in soil suspensions with the pure compounds at concentrations ranging from 1 to 10 mg l −1 . The half-life of metabolite 1 ranged from 3.9 to 5 days, close to the previous values. Metabolite 2 was more persistent and its degradation is strongly dependent on the initial concentration ( C 0): half-life values ranged from 8.1 to 55 days at 2–10 mg l −1 , respectively. These values are higher than those determined from the kinetics of metabolite 1 transformation into metabolite 2 ( t 1/2=8–19 days). The ecotoxicity of the three chemicals was evaluated through their effect on Daphnia magna and Vibrio fischeri (Microtox ® bioassay). No effect was observed on D. magna with 24 and 48 h acute toxicity tests. Similarly, no toxic effect was observed with the Microtox ® test for the three chemicals in the range of concentrations tested that included the field application dose. Thus, being of low persistence and lacking acute toxicity, these chemicals present a low environmental risk. 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An HPLC–DAD method was adapted to simultaneously identify and quantify rimsulfuron and its metabolites, which was successfully validated by GC–MS analysis. In aqueous solutions, pure rimsulfuron was rapidly hydrolyzed into metabolite 1 ( N-(4,6-dimethoxypyrimidin-2-yl)- N-(3-(ethylsulfonyl)-2-pyridinylurea)), which itself was transformed into the more stable metabolite 2 ( N-((3-(ethylsulfonyl)-2-pyridinyl)-4,6-dimethoxy-2-pyrimidineamine)), with half-life ( t 1/2) values of 2 and 2.5 days, respectively. Hydrolysis was instantaneous under alkaline conditions (pH = 10). In aqueous suspensions of the alluvial soil (pH = 8), formulated rimsulfuron had a half-life of 7 days, whereas that of metabolite 1 was similar to that in water (about 3.5 days). The degradation of the two major metabolites was also studied in soil suspensions with the pure compounds at concentrations ranging from 1 to 10 mg l −1 . The half-life of metabolite 1 ranged from 3.9 to 5 days, close to the previous values. Metabolite 2 was more persistent and its degradation is strongly dependent on the initial concentration ( C 0): half-life values ranged from 8.1 to 55 days at 2–10 mg l −1 , respectively. These values are higher than those determined from the kinetics of metabolite 1 transformation into metabolite 2 ( t 1/2=8–19 days). The ecotoxicity of the three chemicals was evaluated through their effect on Daphnia magna and Vibrio fischeri (Microtox ® bioassay). No effect was observed on D. magna with 24 and 48 h acute toxicity tests. Similarly, no toxic effect was observed with the Microtox ® test for the three chemicals in the range of concentrations tested that included the field application dose. Thus, being of low persistence and lacking acute toxicity, these chemicals present a low environmental risk. However, chronic effects should be studied in order to confirm the safety of rimsulfuron and its major metabolites.</abstract><cop>Oxford</cop><pub>Elsevier Ltd</pub><pmid>11680747</pmid><doi>10.1016/S0045-6535(01)00040-6</doi><tpages>8</tpages></addata></record>
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subjects Animal, plant and microbial ecology
Animals
Applied ecology
Biodegradation, Environmental
Biological and medical sciences
Chromatography, High Pressure Liquid
Daphnia
Daphnia magna
Ecotoxicology, biological effects of pollution
Effects of pollution and side effects of pesticides on protozoa and invertebrates
Fundamental and applied biological sciences. Psychology
Gas Chromatography-Mass Spectrometry
Half-Life
Herbicides - metabolism
Herbicides - toxicity
Hydrolysis
Microtox
Pyridines - metabolism
Pyridines - toxicity
rimsulfuron
Risk Assessment
Soil
Soil Microbiology
Sulfonamides - metabolism
Sulfonamides - toxicity
Sulfonylurea
Sulfonylurea Compounds - metabolism
Sulfonylurea Compounds - toxicity
Toxicity Tests
Vibrio
Vibrio fischeri
Water
Water Microbiology
Water Pollutants, Chemical - metabolism
Water Pollutants, Chemical - toxicity
title Degradation in soil and water and ecotoxicity of rimsulfuron and its metabolites
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