Hostname: page-component-76fb5796d-22dnz Total loading time: 0 Render date: 2024-04-27T07:21:42.625Z Has data issue: false hasContentIssue false

Improving chemical control of nonnative aquatic plants in run-of-the-river reservoirs

Published online by Cambridge University Press:  14 July 2022

Ryan M. Wersal*
Affiliation:
Assistant Professor, Department of Biological Sciences, Minnesota State University Mankato, Mankato, MN, USA
Bradley T. Sartain
Affiliation:
Research Biologist, Environmental Laboratory, U.S. Army Engineer Research and Development Center, Vicksburg, MS, USA
Kurt D. Getsinger
Affiliation:
Research Biologist, Environmental Laboratory, U.S. Army Engineer Research and Development Center, Vicksburg, MS, USA
John D. Madsen
Affiliation:
Research Biologist, USDA-ARS ISPHRU, Plant Sciences Department, University of California–Davis, Davis, CA, USA
John G. Skogerboe
Affiliation:
Research Biologist (Retired), Environmental Laboratory, U.S. Army Engineer Research and Development Center, Vicksburg, MS, USA
Justin J. Nawrocki
Affiliation:
Account Manager, United Phosphorus Limited, King of Prussia, PA, USA
Rob J. Richardson
Affiliation:
Professor, Crop Science Department, North Carolina State University, Raleigh, NC, USA
Morgan R. Sternberg
Affiliation:
Research Manager, Morrow BioScience Ltd., Rossland, BC, Canada
*
Author for correspondence:Ryan M. Wersal, Department of Biological Sciences, Minnesota State University, Mankato, Mankato, MN56001. E-mail: ryan.wersal@mnsu.edu

Abstract

Current dam discharge patterns in Noxon Rapids Reservoir reduce concentration and exposure times (CET) of herbicides used for aquatic plant management. Herbicide applications during periods of low dam discharge may increase herbicide CETs and improve efficacy. Applications of rhodamine WT dye were monitored under peak (736 to 765 m3 s−1) and minimum (1.4 to 2.8 m3 s−1) dam discharge patterns to quantify water-exchange processes. Whole-plot dye half-life under minimal discharge was 33 h, a 15-fold increase compared with the dye treatment during peak discharge. Triclopyr concentrations measured during minimum discharge within the treated plot ranged from 214 ± 25 to 1,243 ± 36 µg L−1 from 0 to 48 h after treatment (HAT), respectively. Endothall concentrations measured during minimum discharge in the same plot ranged from 164 ± 78 to 2,195 ± 1,043 µg L−1 from 0 to 48 HAT, respectively. Eurasian watermilfoil (Myriophyllum spicatum L.) occurrence in the treatment plot was 66%, 8%, and 14% during pretreatment, 5 wk after treatment (WAT), and 52 WAT, respectively. Myriophyllum spicatum occurrence in the nontreated plot was 68%, 71%, and 83% during pretreatment, 5 WAT, and 52 WAT, respectively. Curlyleaf pondweed (Potamogeton crispus L.) occurrence in the treatment plot was 29%, 0%, and 97% during pretreatment, 5 WAT, and 52 WAT, respectively. Potamogeton crispus increased from 24% to 83% at 0 WAT to 52 WAT, respectively, in the nontreated plot. Native species richness declined from 3.3 species per point to 2.1 in the treatment plot in the year of treatment but returned to pretreatment numbers by 52 WAT. Native species richness did not change during the study in the nontreated reference plot. Herbicide applications during periods of low flow can increase CETs and improve control, whereas applications during times of high-water flow would shorten CETs and could result in reduced treatment efficacy.

Type
Case Study
Copyright
© The Author(s), 2022. Published by Cambridge University Press on behalf of the Weed Science Society of America

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

Footnotes

Associate Editor: Elizabeth LaRue, The University of Texas at El Paso

References

Fox, AM, Haller, WT, Getsinger, KD (1993) Correlation of endothall and fluorescent dye concentrations following concurrent application to tidal canals. Pest Sci 37:99106 CrossRefGoogle Scholar
Fox, AM, Haller, WT, Getsinger, KD, Petty, DG (2002) Dissipation of triclopyr herbicide applied in Lake Minnetonka, MN concurrently with rhodamine WT dye. Pest Manag Sci 58:677686 CrossRefGoogle ScholarPubMed
Getsinger, KD, Fox, AM, Haller, WT (1996) Herbicide Application Technique Development for Flowing Water: Summary of Research Accomplishments. MP A-96-3. Vicksburg, MS: U.S. Army Engineer Waterways Experiment Station. 16 pGoogle Scholar
Getsinger, KD, Netherland, MD (1997) Herbicide Concentration/Exposure Time Requirements for Controlling Submersed Aquatic Plants: Summary of Research Accomplishments. MP A-97-2. Vicksburg, MS: U.S. Army Engineer Waterways Experiment Station. 18 pGoogle Scholar
Getsinger, KD, Netherland, MD, Grue, CE, Koschnick, TJ (2008) Improvements in the use of aquatic herbicides and future research directions. J Aquat Plant Manag 46:3241 Google Scholar
Getsinger, KD, Petty, DG, Madsen, JD, Skogerboe, JG, Houtman, BA, Haller, WT, Fox, AM (2000) Aquatic dissipation of the herbicide triclopyr in Lake Minnetonka, Minnesota. Pest Manag Sci 56:388400 3.0.CO;2-U>CrossRefGoogle Scholar
Getsinger, KD, Skogerboe, JG, Madsen, JD, Wersal, RM, Nawrocki, JJ, Richardson, RJ, Sterberg, MR (2013) Selective Control of Eurasian Watermilfoil and Curlyleaf Pondweed in Noxon Rapids Reservoir, Montana: Aquatic Herbicide Evaluations, 2009–2010. ERDC/EL TR-13-5. Vicksburg, MS: U.S. Army Engineer Waterways Experiment Station. 97 pCrossRefGoogle Scholar
Getsinger, KD, Turner, EG, Madsen, JD, Netherland, MD (1997) Restoring native vegetation in a Eurasian watermilfoil dominated plant community using the herbicide triclopyr. Regul Riv 13:357375 3.0.CO;2-#>CrossRefGoogle Scholar
Littell, RC, Milliken, GA, Stroup, WW, Wolfinger, RD (1996) SAS® System for Mixed Models. Cary, NC: SAS Institute. 608 pGoogle Scholar
Madsen, JD, Cheshier, JC (2009) Eurasian Watermilfoil Survey of Three Reservoirs in the Lower Clark Fork River, Montana: I. Results of the Field Vegetation Survey. Geosystems Research Institute Report 5033. 59 pGoogle Scholar
Madsen, JD, Stewart, RM, Getsinger, KD, Johnson, RL, Wersal, RM (2008) Aquatic plant communities in Waneta Lake and Lamoka Lake, New York. Northeast Nat 15:97110 CrossRefGoogle Scholar
Madsen, JD, Sutherland, JW, Bloomfield, JA, Eichler, LW, Boylen, CW (1991) The decline of native vegetation under dense Eurasian watermilfoil canopies. J Aquat Plant Manag 29:9499 Google Scholar
Madsen, JD, Wersal, RM (2009) Aquatic Plant Community and Eurasian Watermilfoil (Myriophyllum spicatum L.) Management Assessment in Lake Pend Oreille, Idaho for 2008. Geosystems Research Institute Report 5032. 65 pGoogle Scholar
Madsen, JD, Wersal, RM (2017) A review of aquatic plant monitoring and assessment methods. J Aquat Plant Manag 55:112 Google Scholar
Madsen, JD, Wersal, RM, Getsinger, KD, Skogerboe, JG (2010) Combinations of Endothall with 2,4-D and Triclopyr for Eurasian Watermilfoil Control. ERDC/TN APCRP-CC-14. Vicksburg, MS: U.S. Army Engineer Research and Development Center. 10 pGoogle Scholar
Madsen, JD, Wersal, RM, Woolf, TE (2015) Operational control of Eurasian watermilfoil and impacts to the submersed aquatic macrophyte community in Lake Pend Oreille, ID. Invasive Plant Sci Manag 8:219232 CrossRefGoogle Scholar
Netherland, MD, Getsinger, KD (1992) Efficacy of triclopyr on Eurasian watermilfoil: concentration and exposure time effects. J Aquat Plant Manag 30:15 Google Scholar
Netherland, MD, Green, WR, Getsinger, KD (1991) Endothall concentration and exposure time relationships for the control of Eurasian watermilfoil and hydrilla. J Aquat Plant Manag 29:6167 Google Scholar
Netherland, MD, Skogerboe, JG, Owens, CS, Madsen, JD (2000) Influence of water temperature on the efficacy of diquat and endothall versus curlyleaf pondweed. J Aquat Plant Manag 38:2532 Google Scholar
Poovey, AG, Getsinger, KD, Skogerboe, JG (2004) Small-plot, low-dose treatments of triclopyr for selective control of Eurasian watermilfoil. Lake Reserv Manag 20:322332 CrossRefGoogle Scholar
Poovey, AG, Skogerboe, JG, Owens, CS (2002) Spring treatments of diquat and endothall for curlyleaf pondweed control. J Aquat Plant Manag 40:6367 Google Scholar
Skogerboe, JG, Getsinger, KD (2002) Endothall species selectivity evaluation: northern latitude aquatic plant community. J Aquat Plant Manag 40:15 Google Scholar
Skogerboe, JG, Getsinger, KD (2006) Selective Control of Eurasian Watermilfoil and Curlyleaf Pondweed Using Low Doses Of Endothall Combined with 2,4-D. ERDC/TN APCRP-CC-05. Vicksburg, MS: U.S. Army Engineer Research and Development Center. 15 pGoogle Scholar
Skogerboe, JG, Poovey, AG, Getsinger, KD, Crowell, W, Macbeth, E (2008) Early-Season, Low-Dose Applications of Endothall to Selectively Control Curlyleaf Pondweed in Minnesota Lakes. ERDC/TN APCRP-CC-08. Vicksburg, MS: U.S. Army Engineer Research and Development Center. 14 pGoogle Scholar
Stokes, ME, Davis, CS, Koch, GG (2000) Categorical Data Analysis Using the SAS® System. 2nd ed. Cary, NC: SAS Institute Inc. 648 pGoogle Scholar
Turner, EG, Getsinger, KD, Netherland, MD (1994) Correlation of triclopyr and rhodamine WT dye in the Pend Oreille River. J Aquat Plant Manag 32:3941 Google Scholar
Wersal, RM, Madsen, JD, Cheshier, JC (2009) Eurasian Watermilfoil Monitoring and Mapping in Noxon Rapids Reservoir in 2009. Geosystems Research Institute Report 5041. 11 pGoogle Scholar
Wersal, RM, Madsen, JD, McMillan, , Gerard, PD (2006) Environmental factors affecting biomass and distribution of Stuckenia pectinata in the Heron Lake System, Minnesota, USA. Wetlands 26:313321 CrossRefGoogle Scholar
Wersal, RM, Madsen, JD, Woolf, TE, Eckberg, N (2010) Assessment of herbicide efficacy on Eurasian watermilfoil and impacts to the native submersed plant community in Hayden Lake, Idaho, USA. J Aquat Plant Manag 48:511 Google Scholar
Woolf, TE, Madsen, JD (2003) Seasonal biomass and carbohydrate allocation patterns in southern Minnesota curlyleaf pondweed populations. J Aquat Plant Manag 41:113118 Google Scholar