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Movement and degradation of aldicarb residues in South Carolina loamy sand soil
Institution:1. Clemson University, Clemson, SC 29634, U.S.A.;2. Union Carbide Agricultural Products Co. Inc., Research Triangle Park, NC 27709, U.S.A.;1. Department of Agronomy, Iowa State University, Agronomy Hall, Ames, IA 50011, United States;2. National Laboratory for Agriculture and the Environment, USDA-ARS, 2150 Pammel Drive, Ames, IA 50011, United States;1. Instituto Nacional de Investigación y Tecnología Agraria y Alimentaria (INIA-INAGEA), Dpto. Medio Ambiente y Agronomía, Ctra. de la Coruña km 7,5, 28040 Madrid, Spain;2. Centro de Estudios e Investigación para la Gestión de Riesgos Agrarios y Medioambientales, CEIGRAM-UPM, Senda del Rey 13, 28040 Madrid, Spain;3. Universidad Politécnica de Madrid, Departamento de Producción Agraria, Avda. Puerta de Hierro 2-4, 28040 Madrid, Spain;1. Department of Anesthesiology and Pain Medicine, Seoul National University College of Medicine, Seoul National University Hospital, 101 Daehak-Ro Jongno-Gu, Seoul, 03080, South Korea;2. Department of Information Statistics, Andong National University, 1375 Gyeongdong-Ro Andong, Gyeongsangbuk-do, 36729, South Korea;3. Department of Statistics, Kyungpook National University, 80 Daehak-Ro, Daegu, 41566, South Korea
Abstract:The movement and degradation of aldicarb (2-methyl-2-(methylthio)propionaldehyde O-(methylcarbamoyl)oxime) residues was measured in a Dotham loamy sand soil in Barnwell County in southern South Carolina. The experiment was designed to compare movement in a fallow plot versus a soya bean plot and to compare residue results from soil suction lysimeters and soil samples. The soil sample data indicate that aldicarb degraded at a rate corresponding to a half life of approximately 9 days with essentially no residues present 4 months after application. This degradation rate is faster than the 14–39-day half-life measured in nearby states. Because this relatively rapid degradation rate generally constrained residue movement to the upper 0.3 m in both plots (resulting in no significant residues in the lysimeters and monitoring wells), comparison between data from soil cores and suction lysimeters was not possible and the reduced evapotranspiration in the fallow plot had little effect on residue movement. Simulations using the unsaturated zone model PRZM with rainfall records from 15 years were used to illustrate that aldicarb residues should be limited to the upper 1.5 m, regardless of year-to-year variations in rainfall.
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