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Small-Grain Cover Crops Have Limited Effect on Neonicotinoid Contamination from Seed Coatings

  • Kirsten A. Pearsons*
    Kirsten A. Pearsons
    Department of Entomology, The Pennsylvania State University, University Park, Pennsylvania 16802, United States
    *Email: [email protected]
  • Elizabeth K. Rowen
    Elizabeth K. Rowen
    Department of Entomology, The Pennsylvania State University, University Park, Pennsylvania 16802, United States
  • Kyle R. Elkin
    Kyle R. Elkin
    United States Department of Agriculture—Agricultural Research Service, Pasture Systems and Watershed Management Research Unit, University Park, Pennsylvania 16802, United States
  • Kyle Wickings
    Kyle Wickings
    Department of Entomology, Cornell University, Cornell AgriTech, Geneva, New York 14456, United States
  • Richard G. Smith
    Richard G. Smith
    Department of Natural Resources and the Environment, University of New Hampshire, Durham, New Hampshire 03824, United States
  • , and 
  • John F. Tooker
    John F. Tooker
    Department of Entomology, The Pennsylvania State University, University Park, Pennsylvania 16802, United States
Cite this: Environ. Sci. Technol. 2021, 55, 8, 4679–4687
Publication Date (Web):March 22, 2021
https://doi.org/10.1021/acs.est.0c05547
Copyright © 2021 American Chemical Society

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    Abstract

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    Neonicotinoids from insecticidal seed coatings can contaminate soil in treated fields and adjacent areas, posing a potential risk to nontarget organisms and ecological function. To determine if cover crops can mitigate neonicotinoid contamination in treated and adjacent areas, we measured neonicotinoid concentrations for three years in no-till corn-soybean rotations, planted with or without neonicotinoid seed coatings, and with or without small grain cover crops. Although neonicotinoids were detected in cover crops, high early season dissipation provided little opportunity for winter-planted cover crops to absorb significant neonicotinoid residues; small grain cover crops failed to mitigated neonicotinoid contamination in either treated or untreated plots. As the majority of neonicotinoids from seed coatings dissipated shortly after planting, residues did not accumulate in soil, but persisted at concentrations below 5 ppb. Persistent residues could be attributed to historic neonicotinoid use and recent, nearby neonicotinoid use. Tracking neonicotinoid concentrations over time revealed a large amount of local interplot movement of neonicotinoids; in untreated plots, contamination was higher when plots were less isolated from treated plots.

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    The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acs.est.0c05547.

    • Additional methods details for neonicotinoid extraction and analysis; Table S1, cash crop planting details; Table S2, cover crop planting details; Figure S1, plot maps and relative locations of the North field and South field; Table S3, HPLC gradient and MS settings; Figures S2 and S3, heatmaps of imidacloprid, clothianidin, and thiamethoxam concentrations in the fields across time; Table S4, model summaries for soil concentrations of the most recently applied neonicotinoids in treated (PPM) and control plots; Figures S4 and S5, soil concentrations of the most recently applied neonicotinoids across time; Table S5, number of storm events between planting and taking the first postplant soil samples, and cumulative rainfall during the first week after planting and between planting and soil sampling; Table S6, ANOVA tables for effect of cover on total neonicotinoid dissipation; and Table S7, ANOVA tables for effect of cover on clothianidin dissipation (DOC)

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