Persistence of the sulfonylurea herbicides thifensulfuron-methyl, ethametsulfuron-methyl, and metsulfuron-methyl in farm dugouts (ponds).
Sulfonylurea herbicides are applied at relatively low rates (3 to 40 g ha(-1)) to control weeds in a variety of crops across the Canadian prairies. Because of their high phytotoxicity and the likelihood of their transport in surface runoff, there is concern about their possible impact to aquatic ecosystems. Little is known, however, about their persistence and behavior in aquatic ecosystems. To assess persistence in aquatic ecosystems, three prairie farm dugouts (ponds) were fortified with either thifensulfuron-methyl {methyl 3-[[[[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)amino]carbonyl]amino]sulfonyl]-2-thiophenecarboxylate}, ethametsulfuron-methyl {methyl 2-[[[[[4-ethoxy-6-(methylamino)-1,3,5-triazin-2-yl]amino]carbonyl]amino]sulfonyl]benzoate} or metsulfuron-methyl {methyl 2-[[[[(4-methoxy-6-methyl-1,3,5-triazinyl)amino]carbonyl]amino]sulfonyl]benzoate}. The decreasing order of persistence of environmentally relevant concentrations (1 to 4.6 microg L(-1)) of these herbicides in dugout water over the June to October period was metsulfuron-methyl>ethametsulfuron-methyl>thifensulfuron-methyl. The corresponding dissipation half-lives (DT(50)) of 84, 30, and 16 d, respectively, are in the same relative order as the recropping intervals for these herbicides. Thifensulfuron-methyl showed a biphasic dissipation with slower dissipation during the winter months. In contrast, the dissipation of metsulfuron-methyl, the sulfonylurea herbicide with the longest DT(50), was somewhat enhanced under winter conditions. One of the major routes of sulfonylurea herbicide dissipation was removal from the water column when dugout water was lost during hydrological discharge. The relatively long persistence of these herbicides in water indicates that partitioning into sediments was minimal, the sulfonylurea and methyl ester linkages in these compounds were resistant to hydrolysis in weakly alkaline waters, and that microbial and photolytic degradation in dugout waters were slow.
Cessna
Allan J
AJ
Environment Canada, 300-2365 Albert St., Regina, SK, Canada. allan.cessna@ec.gc.ca
Donald
David B
DB
Bailey
Jonathan
J
Waiser
Marley
M
Headley
J V
JV
D000383:Agriculture; D001190:Arylsulfonates / Q000378:metabolism*; D001565:Benzoates / Q000378:metabolism*; D004784:Environmental Monitoring; D004952:Esters / Q000737:chemistry / Q000378:metabolism; D005618:Fresh Water / Q000737:chemistry*; D006540:Herbicides / Q000378:metabolism*; D006863:Hydrogen-Ion Concentration; D006868:Hydrolysis; D010782:Photolysis; D012621:Seasons; D012988:Soil Microbiology; D013453:Sulfonylurea Compounds / Q000737:chemistry / Q000378:metabolism*; D013876:Thiophenes / Q000378:metabolism*; D013997:Time Factors; D014227:Triazines / Q000378:metabolism*; D014874:Water Pollutants, Chemical / Q000378:metabolism*
D001190:Arylsulfonates; D001565:Benzoates; D004952:Esters; D006540:Herbicides; D013453:Sulfonylurea Compounds; D013876:Thiophenes; D014227:Triazines; D014874:Water Pollutants, Chemical; C050296:metsulfuron methyl; C414314:thifensulfuron methyl; C413983:methyl 2-(((((4-ethoxy-6-(methylamino)-1,3,5-triazin-2-yl)amino)carbonyl)amino)sulfonyl)benzoate