Seed treatments containing neonicotinoids and fungicides reduce aquatic insect richness and abundance in midwestern USA-managed floodplain wetlands.
Autor: | Kuechle KJ; Missouri Cooperative Fish and Wildlife Research Unit, School of Natural Resources, University of Missouri, Columbia, MO, 65211, USA. kkuechle@ducks.org.; Great Plains Regional Office, Ducks Unlimited, Inc, 2525 River Road, Bismarck, ND, 58503, USA. kkuechle@ducks.org., Webb EB; Missouri Cooperative Fish and Wildlife Research Unit, School of Natural Resources, University of Missouri, Columbia, MO, 65211, USA.; U.S. Geological Survey, Missouri Cooperative Fish and Wildlife Research Unit, Columbia, MO, 65211, USA., Mengel D; Missouri Department of Conservation, Science Branch, Columbia, MO, 65201, USA., Main AR; Missouri Cooperative Fish and Wildlife Research Unit, School of Natural Resources, University of Missouri, Columbia, MO, 65211, USA.; Department of Pesticide Regulation, California Environmental Protection Agency, Sacramento, CA, 95812, USA. |
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Jazyk: | angličtina |
Zdroj: | Environmental science and pollution research international [Environ Sci Pollut Res Int] 2022 Jun; Vol. 29 (30), pp. 45261-45275. Date of Electronic Publication: 2022 Feb 10. |
DOI: | 10.1007/s11356-022-18991-9 |
Abstrakt: | Agrochemicals including neonicotinoid insecticides and fungicides are frequently applied as seed treatments on corn, soybeans, and other common row crops. Crops grown from pesticide-treated seed are often directly planted in managed floodplain wetlands and used as a soil disturbance or food resource for wildlife. We quantified invertebrate communities within mid-latitude floodplain wetlands and assessed their response to use of pesticide-treated seeds within the floodplain. We collected and tested aqueous and sediment samples for pesticides in addition to sampling aquatic invertebrates from 22 paired wetlands. Samples were collected twice in 2016 (spring [pre-water level drawdown] and autumn [post-water level flood-up]) followed by a third sampling period (spring 2017). Meanwhile, during the summer of 2016, a portion of study wetlands were planted with either pesticide-treated or untreated corn seed. Neonicotinoid toxic equivalencies (NI-EQs) for sediment (X̅ = 0.58 μg/kg), water (X̅ = 0.02 μg/L), and sediment fungicide concentrations (X̅ = 0.10 μg/kg) were used to assess potential effects on wetland invertebrates. An overall decrease in aquatic insect richness and abundance was associated with greater NI-EQs in wetland water and sediments, as well as with sediment fungicide concentration. Post-treatment, treated wetlands displayed a decrease in insect taxa-richness and abundance before recovering by the spring of 2017. Information on timing and magnitude of aquatic insect declines will be useful when considering the use of seed treatments for wildlife management. More broadly, this study brings attention to how agriculture is used in wetland management and conservation planning. (© 2022. The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature.) |
Databáze: | MEDLINE |
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