Abstract
Neonicotinoid insecticides have been reported to occur widely in surface waters, including those of wetlands within the Prairie Pothole Region (PPR). In the US portion of the PPR, the US Fish and Wildlife Service has established Waterfowl Production Areas (WPAs) in an effort to enhance waterfowl production. Most WPAs have an area of protected upland surrounding wetlands that can act as a buffer to reduce the transport of contaminants, including pesticides. We assessed the extent that neonicotinoid insecticides occurred in the ponded water of wetlands within WPAs located along a gradient of agricultural influence throughout west-central Minnesota. Of the five neonicotinoids we tested for, two were not detected. However, at least one of the other three, imidacloprid, clothianidin and thiamethoxam, were detected in 29% of our wetland water samples. Additionally, both the occurrence and total concentrations of neonicotinoids were higher in sites with higher surrounding crop use. Neonicotinoid insecticides, if persistent for long periods of time, have the potential to affect aquatic-invertebrate communities within PPR wetlands. Our research indicates that areas often perceived as protected may still be at risk to neonicotinoid contamination, emphasizing the importance of maintaining effective grassland buffers around wetlands.
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References
Anderson TA, Salice CJ, Erickson RA, McMurry ST, Cox SB, Smith LM (2013) Effects of landuse and precipitation on pesticides and water quality in playa lakes of the southern high plains. Chemosphere 92:84–90. https://doi.org/10.1016/j.chemosphere.2013.02.054
Beyer H (2015) Geospatial modelling environment. Available via http://www.spatialecology.com/gme/index.htm. Accessed 15 Aug 2017
Cavallaro MC, Morrissey CA, Headley JV, Peru KM, Luber K (2017) Comparative chronic toxicity of imidacloprid, clothianidin, and thiamethoxam to Chironomus dilutus and estimation of toxic equivalency factors. Environmental Toxicology and Chemistry 36:372–382. https://doi.org/10.1002/etc.3536
Chrétien F, Giroux I, Thériault G, Gagnon P, Corriveau J (2017) Surface runoff and subsurface tile drain losses of neonicotinoids and companion herbicides at edge-of-field. Environmental Pollution 224:255–264. https://doi.org/10.1016/j.envpol.2017.02.002
Cox RR Jr, Hanson MA, Roy CC, Euluss NH, Johnson DH, Butler MG (1998) Mallard duckling growth and survival in relation to aquatic invertebrates. Journal of Wildlife Management 62:124–133. https://doi.org/10.2307/3802270
Dahl TE (2014) Status and trends of wetlands in the conterminous United States 2004 to 2009. US Department of the Interior, US Fish and Wildlife Service, Washington
Danell K, Sjöberg K (1977) Seasonal emergence of chironomids in relation to egglaying and hatching of ducks in a restored lake (northern Sweden). Wildfowl 28:129–135
Donald DB, Syrgiannis J, Hinter F, Weiss G (1999) Agricultural pesticides threaten the ecological integrity of norhtern prairie wetlands. Science of the Total Environment 231:173–181
Douglas MR, Tooker JF (2015) Large-scale deployment of seed treatments has driven rapid increase in use of neonicotinoid insecticides and preemptive pest management in U.S. field crops. Environmental Science & Technology 49:5088–5097. https://doi.org/10.1021/es506141g
ECOMAP (1993) National hierarchical framework of ecological units. USDA Forest Service, Washington, DC
Erwin KL (2009) Wetlands and global climate change: the role of wetland restoration in a changing world. Wetlands Ecology and Management 17:71–84. https://doi.org/10.1007/s11273-008-9119-1
Evelsizer V, Skopec M (2016) Pesticides, including neonicotinoids, in drained wetlands of Iowa’s prairie pothole region. Wetlands 38:221–232. https://doi.org/10.1007/s13157-016-0796-x
Goulson D (2013) REVIEW: an overview of the environmental risks posed by neonicotinoid insecticides. Journal of Applied Ecology 50:977–987. https://doi.org/10.1111/1365-2664.12111
Guntenspergen G, Peterson S, Leibowitz SG, Cowardin L (2002) Indicators of wetland condition for the prairie pothole region of the United States. Environmental Monitoring and Assessment 78:229–252
Hallmann CA, Foppen RPB, Turnhout CAMV et al (2014) Declines in insectivorous birds are associated with high neonicotinoid concentrations. Nature 511:341–343. https://doi.org/10.1038/nature13531
Hladik ML, Kolpin DW (2016) First national-scale reconnaissance of neonicotinoid insecticides in streams across the USA. Environment and Chemistry 13:12–20. https://doi.org/10.1071/en15061
Hladik ML, Kolpin DW, Kuivila KM (2014) Widespread occurrence of neonicotinoid insecticides in streams in a high corn and soybean producing region, USA. Environmental Pollution 193:189–196. https://doi.org/10.1016/j.envpol.2014.06.033
Hladik ML, Vandever M, Smalling KL (2016) Exposure of native bees foraging in an agricultural landscape to current-use pesticides. Science of the Total Environment 542:469–477. https://doi.org/10.1016/j.scitotenv.2015.10.077
Houlahan JE, Keddy PA, Makkay K, Findlay CS (2006) The effects of adjacent land use on wetland species richness and community composition. Wetlands 26:79–96. https://doi.org/10.1672/0277-5212(2006)26[79:teoalu]2.0.co;2
Jeschke P, Nauen R, Schindler M, Elbert A (2011) Overview of the status and global strategy for neonicotinoids. Journal of Agricultural and Food Chemistry 59:2897–2908. https://doi.org/10.1021/jf101303g
Krupke CH, Hunt GJ, Eitzer BD, Andino G, Given K (2012) Multiple routes of pesticide exposure for honey bees living near agricultural field. PLoS One 7(1):e29268s. https://doi.org/10.1371/journal.pone.0029268
Main AR, Headley JV, Peru KM, Michel NL, Cessna AJ, Morrissey CA (2014) Widespread use and frequent detection of neonicotinoid insecticides in wetlands of Canada’s Prairie Pothole Region. PLoS One 9(6):e101400. https://doi.org/10.1371/journal.pone.0092821
Main AR, Michel NL, Headley JV, Peru KM, Morrissey CA (2015) Ecological and landscape drivers of neonicotinoid insecticide detections and concentrations in Canada’s prairie wetlands. Environmental Science & Technology 49:8367–8376. https://doi.org/10.1021/acs.est.5b01287
Main AR, Michel NL, Cavallaro MC, Headley JV, Peru KM, Morrissey CA (2016) Snowmelt transport of neonicotinoid insecticides to Canadian prairie wetlands. Agriculture, Ecosystems and Environment 215:76–84. https://doi.org/10.1016/j.agee.2015.09.011
Main AR, Fehr J, Liber K, Headley JV, Peru KM, Morrissey CA (2017) Reduction of neonicotinoid insecticide residues in prairie wetlands by common wetland plants. Science of the Total Environment 579:1193–1202. https://doi.org/10.1016/j.scitotenv.2016.11.102
Maloney EM, Morrissey CA, Headley JV, Peru KM, Liber K (2017) Cumulative toxicity of neonicotinoid insecticide mixtures to Chironomus dilutus under acute exposure scenarios. Environmental Toxicology and Chemistry 36:3091–3101. https://doi.org/10.1002/etc.3878
Mclaughlin A, Mineau P (1995) The impact of agricultural practices on biodiversity. Agriculture, Ecosystems and Environment 55:201–212. https://doi.org/10.1016/0167-8809(95)00609-v
Meehan TD, Werling BP, Landis DA, Gratton C (2011) Agricultural landscape simplification and insecticide use in the Midwestern United States. Proceedings of the National Academy of Sciences 108:11500–11505. https://doi.org/10.1073/pnas.1100751108
Morrissey CA, Mineau P, Devries JH, Sanchez-Bayo F, Liess M, Cavallaro MC, Liber K (2015) Neonicotinoid contamination of global surface waters and associated risk to aquatic invertebrates: a review. Environment International 74:291–303. https://doi.org/10.1016/j.envint.2014.10.024
Osborne LL, Kovacic DA (1993) Riparian vegetated buffer strips in water-quality restoration and stream management. Freshwater Biology 29:243–258. https://doi.org/10.1111/j.1365-2427.1993.tb00761.x
R Core Team (2018) R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. URL https://www.R-project.org/
Riens JR, Schwarz MS, Mustafa F, Hoback WW (2013) Aquatic macroinvertebrate communities and water quality at buffered and non-buffered wetland sites on federal waterfowl production areas in the Rainwater Basin, Nebraska. Wetlands 33:1025–1036. https://doi.org/10.1007/s13157-013-0460-7
Simon-Delso N, Amaral-Rogers V, Belzunces LP, Bonmatin JM, Chagnon M, Downs C, Furlan L, Gibbons DW, Giorio C, Girolami V, Goulson D, Kreutzweiser DP, Krupke CH, Liess M, Long E, McField M, Mineau P, Mitchell EAD, Morrissey CA, Noome DA, Pisa L, Settele J, Stark JD, Tapparo A, van Dyck H, van Praagh J, van der Sluijs JP, Whitehorn PR, Wiemers M (2015) Systemic insecticides (neonicotinoids and fipronil): trends, uses, mode of action and metabolites. Environmental Science and Pollution Research 22:5–34. https://doi.org/10.1007/s11356-014-3470-y
Smit CE, Posthuma-Doodeman CJAM, Vlaardingen PLAV, Jong FMWD (2015) Ecotoxicity of imidacloprid to aquatic organisms: derivation of water quality standards for peak and long-term exposure. Human and Ecological Risk Assessment 21:1608–1630. https://doi.org/10.1080/10807039.2014.964071
Sparks TC (2013) Insecticide discovery: an evaluation and analysis. Pesticide Biochemistry and Physiology 107:8–17. https://doi.org/10.1016/j.pestbp.2013.05.012
Starner K, Goh KS (2012) Detections of the neonicotinoid insecticide imidacloprid in surface waters of three agricultural regions of California, USA, 2010–2011. Bulletin of Environmental Contamination and Toxicology 88:316–321. https://doi.org/10.1007/s00128-011-0515-5
Stehle S, Schulz R (2015) Agricultural insecticides threaten surface waters at the global scale. PNAS 112:5750–5755. https://doi.org/10.1073/pnas.1500232112
Stewart, RE, Kantrud HA (1971) Classification of natural ponds and lakes in the glaciated prairie region. Bureau of Sport Fisheries and Wildlife, Resource Publication 92. Washington
Struger J, Grabuski J, Cagampan S, Sverko E, McGoldrick D, Marvin CH (2017) Factors influencing the occurrence and distribution of neonicotinoid insecticides in surface waters of southern Ontario, Canada. Chemosphere 169:516–523. https://doi.org/10.1016/j.chemosphere.2016.11.036
Sur R, Stork A (2003) Uptake, translocation and metabolism of imidacloprid in plants. Bulletin of Insectology 56:35–40
USDA National Agricultural Statistics Service Cropland Data Layer (2012) Published crop-specific data layer. Available via https://nassgeodata.gmu.edu/CropScape/ Accessed May 01 2016
USDA National Agricultural Statistics Service Cropland Data Layer (2013) Published crop-specific data layer. Available via https://nassgeodata.gmu.edu/CropScape/ Accessed May 01 2016
USDA National Agricultural Statistics Service Cropland Data Layer (2014) Published crop-specific data layer. Available via https://nassgeodata.gmu.edu/CropScape/ Accessed May 01 2016
USDA National Agricultural Statistics Service Cropland Data Layer (2015) Published crop-specific data layer. Available via https://nassgeodata.gmu.edu/CropScape/ Accessed May 01 2016
USDA National Acricultural Statistics Service - Minnesota Crop Progress and Condition Report (2017) Published Crop Progress and Condition Reports. Available via https://www.nass.usda.gov/Statistics_by_State/Minnesota/Publications/Crop_Progress_&_Condition/index.php. Accessed April 01 - July 01 2017
USEPA (2018) Aquatic life benchmarks and ecological risk assessments for registered pesticides. U.S. Environmental Protection Agency. Available via https://www.epa.gov/pesticide-science-and-assessing-pesticide-risks/aquatic-life-benchmarks-and-ecological-risk. Accessed May 01 2018
USGS (2014) National water-quality qssessment (NAWQA) program annual P\pesticide use maps. Available via https://waterusgsgov/nawqa/pnsp/usage/maps/. Accessed Sept 15 2017
Van Dijk TC, Staalduinen MAV, Sluijs JPVD (2013) Macro-invertebrate decline in surface water polluted with imidacloprid. PLoS One 8(5):e62374. https://doi.org/10.1371/journal.pone.0062374
Wettstein FE, Kasteel R, Delgado MFG et al (2016) Leaching of the neonicotinoids thiamethoxam and imidacloprid from sugar beet seed dressings to subsurface tile drains. Journal of Agricultural and Food Chemistry 64:6407–6415. https://doi.org/10.1021/acs.jafc.6b02619
Acknowledgments
We thank Sara Vacek and Josh Eash for their assistance and technical support with sample collection for our study. Additionally, we thank the staff at the Morris Wetland Management district for the use of facilities and the hosting of sampling within their district. We would also like to thank Dawn Macdonald and Vince Capeder for their assistance in troubleshooting equipment while in the field. Funding for analyses of our wetland water samples were provided by the U.S. Fish and Wildlife Service. Findings and conclusions in this study are those of the authors and do not necessarily represent the views of the U.S. Fish and Wildlife Service.
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Williams, N., Sweetman, J. Distribution and Concentration of Neonicotinoid Insecticides on Waterfowl Production Areas in West Central Minnesota. Wetlands 39, 311–319 (2019). https://doi.org/10.1007/s13157-018-1090-x
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DOI: https://doi.org/10.1007/s13157-018-1090-x