| Herbicide Rate | - Generally applied in combination with diquat for hydrilla control at concentration in water of 1ppm
- Applied at rates of 0.75-1.0ppm for floating plant control near potable water intakes
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| Breakdown / Inactivation | As an element, copper can persist indefinitely; however, it binds to particulates in water and sediments |
| Adsorption | - Adsorbs to organic materials and clay particles
- Degree of adsorption depends on acidity and alkalinity
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| Dissipation | Generally does not disperse widely in treated waterbodies due to precipitation, settling, adsorption |
| Formulation | |
| Liquid | Available in organic complex called copper chelate designed to keep in solution as long as possible |
| Solid | - Copper sulfate available in crystal formulations; also called blue stone
- Copper chelate available in granulated or pelletized formulations
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Mode of Action
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| Contact | |
| Plant Growth Regulator | Used as herbicide for aquatic plant control applications in FWC programs- Functions as growth inhibitor or growth regulator at lower rates
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| Stewardship | |
| Herbicide resistance | - Resistance reported in blue-green algae after repeated use over decades in Minnesota
- Used occasionally for aquatic plant control in Florida and often in combination with other herbicides
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| Waterbody Parameters | Management Considerations |
| Hydrology | |
| Water depth and volume | Important to maintain prescribed dose; therefore, accurate bathymetry is imperative for hydrilla control |
| Water movement | - Not generally an issue with aquatic plant control use patterns
- Applied to floating plant leaves or with diquat or Aquathol for spot control at boat ramps
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| Water chemistry | |
| Dissolved oxygen (DO) | - May be an issue for large-scale algae control in potable water reservoirs
- Generally not an issue with the small-scale aquatic plant control use patterns in Florida
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| pH, alkalinity, hardness | - In waters with less than 50ppm alkalinity, copper may be toxic to fish at rates applied to control plants
- Copper sulfate precipitates in waters with high alkalinity (greater than 250ppm)
- Copper precipitation less of a concern with chelated copper formulations
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Nutrient content
| Fast acting, but generally not an issue with the small-scale aquatic plant control use patterns in Florida |
| Water transparency | |
| Sediment characteristics | |
| Composition | - Sand/Clay – adsorption to organic particulates and clay sediments
- Organic – adsorption to suspended organic particles
- Avoid applying pellets to deep flocculent organic sediments
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| Potential for resuspension | Avoid disturbing sediments when applying to shallow waters |
| Plant Physiology Parameters | Management Considerations |
| Plant origin/ growth potential | |
| Native | - Used for short-term algae control
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| Non-native | |
| Invasive | - Used for water hyacinth or water lettuce control near potable water intakes
- Used for small-scale or spot control of newly discovered hydrilla populations targeted for eradication
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| Plant growth stage (target/non-target) | Shorter exposure periods may be applicable for young, actively growing plants |
Plant susceptibility (target/non-target)
| - Apply to actively growing target plants
- High rates are required to control floating plants but there are no potable water restrictions
- Fast control when combined with diquat so used to quickly eradicate hydrilla from boat ramp areas
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| Potential for regrowth (target/non-target) | - Provides long-term control of floating plants
- Used for rapid control of new hydrilla populations before hydrilla can establish tubers
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| Climate Parameters | Management Considerations |
| Weather | - Daily
- avoid applications during high wind and wave conditions to minimize turbidity
- Seasonally
- avoid large-scale applications during hot summer months
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| Water temperature | - Fish toxicity increases during hot summer months, especially in waters with low alkalinity
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