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    GIVE UNIVERSITY OF FLORIDA
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    • About the Center
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    • Why Manage Plants?
          • Native Plants
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          • Aquatic and Wetland Plants in Florida
          • Florida’s Most Invasive Plants
          • Why Manage Plants? It’s the Law
    • Florida's Waters
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          • Water Quality
          • Shared Uses and Functions
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    • Control Methods
          • Biological Control
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    • Management Plans
          • Scope of Aquatic Plant Management
          • Biological Control Considerations
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    Center For Aquatic And Invasive Plants

    Center For Aquatic And Invasive Plants

     Section 4 - Header
    • plants.ifas.ufl.edu
    • Management Plans
    • Chemical Control Considerations
    • Diquat Considerations

    Diquat

    NDPES Logo

    *Important: See Reference Guide Beforehand

    No single herbicide is appropriate for controlling all invasive aquatic plants (or nuisance growths of native aquatic plants), in all situations. A herbicide may perform differently depending on the waterbody, its use, the time of year—or even the time of day. Therefore, aquatic plant managers must have a thorough understanding of how each herbicide acts in Florida aquatic systems. The following parameters are evaluated when considering this herbicide to manage aquatic plants in a specific waterbody. Each parameter is linked to an explanation and examples are provided to demonstrate their relevance to developing comprehensive aquatic plant management strategies.

    These considerations are not meant to replace or contradict the EPA approved label.
    Always read and follow the pesticide label for each product used.


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    Table A: Herbicide Use Patterns for Diquat

    Target Plant Scientific Name Use Pattern Compatible Herbicides
    Hydrilla Hydrilla verticillata Frequent Mostly used in combination with potassium endothall; occasionally used alone or in combination with flumioxazin, bispyribac, or topramezone
    Water lettuce Pistia stratiotes Frequent Used alone
    Water hyacinth Eichhornia crassipes Frequent Used alone or in combination with 2,4-D
    Cuban club-rush Cyperus blepharoleptos Frequent Usually in combination with 2,4-D
    Wright’s nutrush Scleria lacustris Occasional Used alone
    Feathered mosquitofern Azolla pinnata Occasional Used alone
    Giant salvinia Salvinia molesta Spot / eradication Used alone

    Table B: Water Uses and Functions

    Water Use Parameters Management Considerations
    Downstream Uses and Needs
    • Water-use restrictions depend on rate
      • 1-3 day restriction for ornamental plant watering
      • 1-5 day restriction for irrigating crops
    Fish and Wildlife Mgmt.  
    Vegetation planting
    • Avoid applications within newly installed aquatic revegetation sites
    Forage and prey
    • Diquat dibromide has a low bioaccumulation potential
    Fisheries
    • Slight to moderate toxicity to fish
      • 8-hour LC50 is 12.3 mg/L for rainbow trout and 28.5 mg/L for Chinook salmon
      • Do not use in waters used for fish protein concentrate or fish meal production
    Non-game wildlife
    • No issues related to this tool
    Endangered species
    • No issues related to this tool
    Waterfowl
    • Moderately toxic to birds
      • Mallard duck oral LD50 is 564 mg/kg
    Flood Control
    • No issues related to this tool
    Navigation and Access
    • No issues related to this tool
    Irrigation
    • Water-use restrictions depend on rate
      • 1-3 day restriction for ornamental plant watering
      • 1-5 day restriction for irrigating crops
    Livestock Consumption
    • 1-day water-use restriction if treated waterbody is the sole source for watering
    Potable Water
    • Rate-dependent setbacks of 350-1600 feet from functioning potable water intake
      • See label for specific information
      • Within these distances, shut off water intake for 1-3 days depending on rate, or
      • Until concentration falls below 0.02 ppm
    • Coordinate with water facility manager for applications within 1600 feet of an active potable-water intake
    Recreation  
    Boating
    • No issues related to this tool
    Fishing
    • No fish consumption restriction
    • Does not bioaccumulate in fish
    Hunting
    • No issues related to this tool
    Swimming
    • No swimming restriction

    Table C: Herbicide, Waterbody, Plant, and Climate Parameters

    Herbicide Parameters Management Considerations
    Herbicide Rate
    • Maximum label rate for controlling floating plants is 0.75 gpa
      • Generally applied at 0.25 to 0.5 gpa
    • Applied at concentrations up to 0.37 ppm for submersed plant (hydrilla) control
    Breakdown / Inactivation
    • Almost immediately bound to soil or vegetation
    • Tightly bound residues are not biologically available, so the herbicide is deactivated on soil
      • Bound residues are resistant to microbial degradation
      • Soil dissipation half-life exceeds 3 years
    Microbial
    • Broken down slowly by microbes if not bound to sediments
    Adsorption
    • Binds tightly to clay and organic material
      • Do not apply in muddy or turbid waters for submersed plant control
      • Avoid tank mixing with muddy or turbid water before applying to emergent foliage
    Photolysis
    • Broken down slowly by sunlight if not bound to sediments
    Hydrolysis
    • Not sensitive to hydrolysis
    Dissipation
    • Dissipation half-life in water is 1-2 days as diquat is bound to sediment and deactivated
    Formulation  
    Liquid
    • Available in liquid formulation
    Solid
    • Not available in solid formulation
    Mechanism of Action
    • Classified in WSSA Resistance Grouping #22
      • Photosystem I inhibitor
    Mode of Action  
    Contact
    • Fast acting, contact-type herbicide: rapidly absorbed by plant leaves
    • Interferes with cell respiration, the process by which plants take in oxygen
    • Plant tissues are killed too quickly to allow translocation to other parts of the plant
    Plant Growth Regulator
    • Used as herbicide for aquatic plant control applications in FWC programs
    • Functions as growth inhibitor or growth regulator at lower rates
    Stewardship  
    Herbicide resistance
    • Resistance confirmed in Landoltia species of duckweed in Florida
    • Rotate or combine with other compounds where possible
      • Used in combination with endothall for submersed plant control
      • Combine with 2,4-D for mixed water hyacinth / water lettuce populations
    Waterbody Parameters Management Considerations
    Hydrology  
    Water depth
    • Avoid disturbing organic or clay sediments in shallow waters during submersed plant control (binds tightly and is inactivated in turbid waters)
    Water volume
    • Use at rates up to 0.37 ppm for submersed plant control
    • Amounts used are depth-dependent – see label for chart
    Water movement
    • At least 24 hours of contact are required for submersed plant control
    Water chemistry  
    Dissolved oxygen (DO)
    • Fast-acting when used in combination with endothall for submersed plant control
    • Use caution in large-scale treatments in warm water to avoid dissolved oxygen depletion
    • Treat only 1/3 to 1/2 of the water body at one time – wait 14 days between treatments
    pH, alkalinity, hardness
    • No issues related to this tool
    Nutrient content
    • Fast-acting contact type herbicide
    • Nutrients may be released from decomposing plants in large-scale treatments
    Water transparency
    • Color/tannic content: no issues
    • Turbidity: avoid mixing with, or applying to turbid waters
      • Binds tightly to clay and organic particles
    Sediment characteristics  
    Composition
    • Sand: no issues related to this tool
    • Clay: binds tightly to, and is inactivated in waters with suspended clay particles
    • Organic: binds tightly to suspended organic particles and organic sediments
    Potential for re-suspension
    • Avoid stirring flocculent sediments during submersed plant applications
      • Especially in shallow water
    • Avoid drawing clay or organic turbid water for tank mixes using diquat
    Plant Physiology Parameters Management Considerations
    Plant origin / growth potential  
    Native
    • Illinois pondweed (Potamogeton illinoensis), southern naiad (Najas guadalupensis)
      • Occasionally controlled for access or navigation
      • 1.0 ppm potassium endothall + 0.37 ppm diquat
    Non-native
    • Water fern (Salvinia minima)
      • Occasional control for access or navigation in confined areas
      • 0.5-0.75 gpa
    Invasive

     

    • Hydrilla – where suspended organics or clay are not a concern
      • Poor or inconsistent control of hydrilla when used alone
      • 0.37 ppm diquat + 1 ppm potassium endothall (2 ppm endothall for mature hydrilla)
        • Rapid knockdown of hydrilla mat
        • Requires shorter retention time and faster control than endothall alone
        • Resistance management strategy
        • Cutting trails or small exposed bands
        • 0.37 ppm diquat + 0.10 ppm flumioxazin
      • Use in clear, low pH waters due to short flumioxazin half-life in pH > 7
      • Very active on water lilies
      • Resistance management strategy
    • Floating plants (water hyacinth / water lettuce)
      • 1-2 qt/ac for smaller water hyacinth – up to 3 qt/ac for mature “Bull” hyacinth
        • Spray to wet – need complete coverage
      • 1-2 qt/ac for water lettuce
      • 1 qt diquat + 2 qt 2,4-D/ac for hyacinth/lettuce mix and resistance management
    • Cuban club-rush and Wright’s nutrush
      • 2 qt/ac diquat or 1 qt diquat + 2 qt 2,4D/ac
    • Giant salvinia (Salvinia molesta) and Feathered mosquitofern (Azolla pinnata)
      • 2 qt/ac
    Plant growth stage (target/non-target)
    • Apply to actively growing target plants
      • Lower rates may be applicable for young, actively growing plants
    Plant susceptibility (target/non-target)
    • Resistance confirmed in Landoltia species of duckweed in Florida
    • Good efficacy alone or combined with 2,4-D for water hyacinth/water lettuce control
    • Use in place of 2,4-D to control water hyacinth mixed with bulrush (Schoenoplectus spp.)
      • Repeated use or higher doses of 2,4-D are toxic to bulrush
      • Diquat may spot or brown bulrush stems, but they quickly recover
    • Controls some beneficial plants like southern naiad, Illinois pondweed, strapleaf sagittaria (Sagittaria kurziana) Spatter-dock (Nuphar spp.), jointed spikerush (Eleocharis interstincta)
    • Minimize non-target effects by applying when native plants are dormant
      • Or before target plants mature or covers large areas
    Potential for regrowth (target/non-target)
    • Longer term control when applied to actively growing immature hydrilla
    • Temporary injury reported for soft-stem bulrush in greenhouse studies
    Climate Parameters Management Considerations
    Weather Daily
    • Need at least 30 minutes of exposure for floating or emergent plants
    • Need at least 24 hours of contact time for submersed plant control with endothall

    Seasonally

    • Several months of hydrilla control when applied in fall or winter
    • 1-3 months of control when applied to mature hydrilla in warm water
    Light intensity
    • Low intensity may reduce submersed plant ability to recover after application
    Water temperature
    • Apply with water temperature above 50o F to ensure active growth of target plants
      • Plants must be actively growing for plant to take up herbicide
      • Do not apply for hydrilla control if strong thermocline exists
        • Or use deep and shallow trailing hoses to treat the entire water column

    Table D: Other Parameters

    Parameter Management Considerations
    Cost
    • Generics are available
    • Alternate herbicides with equivalent efficacy may be available for some species
    Anticipated Control Amount
    Spatial
    • Contact-type herbicide – generally does not disperse far outside submersed plant treatment area
      • Acres of submersed plants controlled equals area to which diquat (+ endothall) is applied
    • Need to treat the entire water column
    Duration
    • Provides good water hyacinth/water lettuce control
      • Regrowth is generally from seed or new plants drifting from outside control zone
    • Hydrilla control varies (1 to 6 months) based on water temperature and plant growth stage
    Time to Achieve Control
    • Fast-acting
      • Floating plant symptoms within hours after application – control in several days to one week
      • Submersed plant control in 1-2 weeks after application
    Contractor/Equipment
    • Apply by hand gun from airboat for small acreages of floating plants
    • Apply aerially by helicopter for larger acreages of submersed plants
    • Apply with endothall by trailing hoses from airboat for submersed-plant control, especially smaller acreages of hydrilla (1 to 200 acres)
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    UF / IFAS Center for Aquatic and Invasive Plants
    7922 NW 71 Street Gainesville, FL 32653
    (352) 392-9613

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