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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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 |
format | Article |
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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.</description><identifier>ISSN: 0045-6535</identifier><identifier>EISSN: 1879-1298</identifier><identifier>DOI: 10.1016/S0045-6535(01)00040-6</identifier><identifier>PMID: 11680747</identifier><identifier>CODEN: CMSHAF</identifier><language>eng</language><publisher>Oxford: Elsevier Ltd</publisher><subject>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</subject><ispartof>Chemosphere (Oxford), 2001-11, Vol.45 (4), p.515-522</ispartof><rights>2001 Elsevier Science Ltd</rights><rights>2002 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a476t-eb0aab0b74941ba3fb6e408b41f494f0be5c9c68a60e153a7655757c79f22e623</citedby><cites>FETCH-LOGICAL-a476t-eb0aab0b74941ba3fb6e408b41f494f0be5c9c68a60e153a7655757c79f22e623</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/S0045653501000406$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,776,780,3537,27901,27902,65306</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=14126731$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/11680747$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Martins, Jean M.F.</creatorcontrib><creatorcontrib>Chevre, Nathalie</creatorcontrib><creatorcontrib>Spack, Lionel</creatorcontrib><creatorcontrib>Tarradellas, Joseph</creatorcontrib><creatorcontrib>Mermoud, André</creatorcontrib><title>Degradation in soil and water and ecotoxicity of rimsulfuron and its metabolites</title><title>Chemosphere (Oxford)</title><addtitle>Chemosphere</addtitle><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.</description><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>Biodegradation, Environmental</subject><subject>Biological and medical sciences</subject><subject>Chromatography, High Pressure Liquid</subject><subject>Daphnia</subject><subject>Daphnia magna</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Effects of pollution and side effects of pesticides on protozoa and invertebrates</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Gas Chromatography-Mass Spectrometry</subject><subject>Half-Life</subject><subject>Herbicides - metabolism</subject><subject>Herbicides - toxicity</subject><subject>Hydrolysis</subject><subject>Microtox</subject><subject>Pyridines - metabolism</subject><subject>Pyridines - toxicity</subject><subject>rimsulfuron</subject><subject>Risk Assessment</subject><subject>Soil</subject><subject>Soil Microbiology</subject><subject>Sulfonamides - metabolism</subject><subject>Sulfonamides - toxicity</subject><subject>Sulfonylurea</subject><subject>Sulfonylurea Compounds - metabolism</subject><subject>Sulfonylurea Compounds - toxicity</subject><subject>Toxicity Tests</subject><subject>Vibrio</subject><subject>Vibrio fischeri</subject><subject>Water</subject><subject>Water Microbiology</subject><subject>Water Pollutants, Chemical - metabolism</subject><subject>Water Pollutants, Chemical - toxicity</subject><issn>0045-6535</issn><issn>1879-1298</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2001</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkEtv1DAQgC1ERZfCTwDlQkUPKZ7Ej-SEUKG0UiWQgLM1dsbIKBsX24H235PsruixJ4893zz8MfYK-DlwUO--cS5krWQr33I448uN1-oJ20Cn-xqavnvKNv-RY_Y8518LBEr2z9gxgOq4FnrDvn6knwkHLCFOVZiqHMNY4TRUf7FQ2kXkYol3wYVyX0VfpbDN8-jntBSs6VBytaWCNo6hUH7BjjyOmV4ezhP24_LT94ur-ubL5-uLDzc1Cq1KTZYjWm616AVYbL1VJHhnBfjlxXNL0vVOdag4gWxRKym11E73vmlINe0JO933vU3x90y5mG3IjsYRJ4pzNtA1HGSvHgeF4r2WsIByD7oUc07kze3yV0z3BrhZnZudc7MKNRzMzrlZB7w-DJjtloaHqoPkBXhzADA7HH3CyYX8wAlolG7XBd7vOVq8_QmUTHaBJkdDSOSKGWJ4ZJV_iQ-dew</recordid><startdate>20011101</startdate><enddate>20011101</enddate><creator>Martins, Jean M.F.</creator><creator>Chevre, Nathalie</creator><creator>Spack, Lionel</creator><creator>Tarradellas, Joseph</creator><creator>Mermoud, André</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>C1K</scope><scope>SOI</scope><scope>7QH</scope><scope>7TV</scope><scope>7U7</scope><scope>7UA</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>20011101</creationdate><title>Degradation in soil and water and ecotoxicity of rimsulfuron and its metabolites</title><author>Martins, Jean M.F. ; Chevre, Nathalie ; Spack, Lionel ; Tarradellas, Joseph ; Mermoud, André</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a476t-eb0aab0b74941ba3fb6e408b41f494f0be5c9c68a60e153a7655757c79f22e623</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2001</creationdate><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>Biodegradation, Environmental</topic><topic>Biological and medical sciences</topic><topic>Chromatography, High Pressure Liquid</topic><topic>Daphnia</topic><topic>Daphnia magna</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Effects of pollution and side effects of pesticides on protozoa and invertebrates</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Gas Chromatography-Mass Spectrometry</topic><topic>Half-Life</topic><topic>Herbicides - metabolism</topic><topic>Herbicides - toxicity</topic><topic>Hydrolysis</topic><topic>Microtox</topic><topic>Pyridines - metabolism</topic><topic>Pyridines - toxicity</topic><topic>rimsulfuron</topic><topic>Risk Assessment</topic><topic>Soil</topic><topic>Soil Microbiology</topic><topic>Sulfonamides - metabolism</topic><topic>Sulfonamides - toxicity</topic><topic>Sulfonylurea</topic><topic>Sulfonylurea Compounds - metabolism</topic><topic>Sulfonylurea Compounds - toxicity</topic><topic>Toxicity Tests</topic><topic>Vibrio</topic><topic>Vibrio fischeri</topic><topic>Water</topic><topic>Water Microbiology</topic><topic>Water Pollutants, Chemical - metabolism</topic><topic>Water Pollutants, Chemical - toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Martins, Jean M.F.</creatorcontrib><creatorcontrib>Chevre, Nathalie</creatorcontrib><creatorcontrib>Spack, Lionel</creatorcontrib><creatorcontrib>Tarradellas, Joseph</creatorcontrib><creatorcontrib>Mermoud, André</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><collection>Aqualine</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Chemosphere (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Martins, Jean M.F.</au><au>Chevre, Nathalie</au><au>Spack, Lionel</au><au>Tarradellas, Joseph</au><au>Mermoud, André</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Degradation in soil and water and ecotoxicity of rimsulfuron and its metabolites</atitle><jtitle>Chemosphere (Oxford)</jtitle><addtitle>Chemosphere</addtitle><date>2001-11-01</date><risdate>2001</risdate><volume>45</volume><issue>4</issue><spage>515</spage><epage>522</epage><pages>515-522</pages><issn>0045-6535</issn><eissn>1879-1298</eissn><coden>CMSHAF</coden><abstract>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.</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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language | eng |
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source | MEDLINE; Elsevier ScienceDirect Journals |
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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