MAIN INDEX |
Manual removal or cutting |
Water level manipulation and drawdowns |
Light barriers |
Bottom "benthic" barriers |
Nutrient alteration |
Sediment (muck) removal, dredging |
Fire |
Aeration |
You can join in! |
Prevention |
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THE PHYSICAL CHARACTERISTICS OF A WATER BODY AND SURROUNDING WETLAND HELP DETERMINE the composition of the aquatic and wetland plant communities that inhabit them. Slight environmental changes in water level, temperature and light penetration can severely stress or even kill an entire plant population within the water body.
Aquatic plant managers have learned that physically manipulating plants and the environment they are in can help managers control certain plant species.
Besides literally hand-yanking them out of the ground or water, or cutting them with a hand-held blade, invasive plants can also be controlled by artificial environmental alterations such as water level manipulation, dredging, light barriers and dyes, bottom barriers, nutrient alteration, aeration and prescribed fire.
These are all referred to as "physical, and sometimes cultural, controls".
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Manual Removal or Cutting
Hand pulling requires laborers to dig out the entire plant and its roots. Plant material is then deposited away from the shoreline. Pulling is a practical control method if small amounts of aquatic plants are easily accessible and in water less than a few feet deep. Otherwise the process may require the assistance of trained scuba divers.
The effectiveness of pulling depends on sediment type, water visibility and thoroughness of removal. A high degree of control lasting more than one season is possible depending upon the species of plant and if complete removal can be achieved.
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A variation of hand-pulling is "diver-assisted dredging." Divers working in deep water hand-pull plants and feed them into a 4" flexible hose. The hose is connected to a vacuum pump, situated in more shallow water, which draws up both water and plant material. Diver-assisted dredging has been used in Florida only in the fast moving waters of the Wakulla River to dredge hydrilla from small, high use areas. In such areas machine harvesting would not be possible and herbicide applications would not be effective.
Advantages to pulling are: control can be selective; control is immediate, and control can be accomplished in sensitive and in hard-to-reach areas. Hand-pulling is usually employed where other methods have not been successful, such as in fast-flowing water, shallow waters.
However, pulling is labor intensive, must be conducted on a routine basis, is limited to low density and small areas. Hand-pulling may also result in a temporary increase in water turbidity. Special consideration must be taken with plants such hydrilla and other plants that reproduce by fragments in order to avoid loose fragments that could colonize other areas within an infested water body, or other water bodies.
Hand cutting requires the use of tools such as rakes, chains, logs, railroad ties, or even old bedsprings, which are pulled through the weed beds in order to sever the plant from the sediment.
Hand-cutting is less labor-intensive than hand-pulling because roots are not removed. Advantages to cutting are immediate removal; minimal cost in small areas; site specificity; and species specificity. Hand-cutting minimizes environmental disruption if done with care. Still, the results are usually short term. Rapid regrowth is possible and the effects of cutting generally last less than one growing season. Cutting is time consuming and labor intensive. It also increases water turbidity. Fragments are numerous and messy; hand-cutting is not practical for large areas.
Water Level Manipulation and Drawdowns
Aquatic vegetation may be controlled artificially by manipulating water levels. Raising water levels can either drown
emersed plants or strand floating plants in upland areas. Alternatively lowering water levels,
a technique known "drawdown," can be used to expose emersed, submersed, and floating plants to
freezing and drying. Water level manipulation techniques are limited to closed water bodies such as lakes,
ponds, canals, and reservoirs.
Drawdowns, or dewatering, have been used for many centuries as a means to oxidize
and consolidate sediments, alter fish populations, and to control aquatic
weeds. The technique requires a dam or other mechanism to lower water levels. The process may
be restricted by water use patterns, water rights, or the lack of a predictable source of water for
refilling. Drawdowns generally take place in winter to take advantage of drier weather, freezes,
and prescribed fire
to further stress target plants. Consecutive drawdowns are more successful than a single
drawdown.
Drawdown success is determined by:
However, drawdown does not always produce desirable results. Responses can be unpredictable.
For example, Brazilian elodea (Egeria
densa) is easily controlled by drawdown and
control may last several years. Hydrilla (Hydrilla verticillata) is only partially
controlled by drawdown and hydrilla's underground tubers can survive several drawdowns,
resprouting and overwhelming the native plants as soon as the water body is refilled.
Water hyacinth and water lettuce can be controlled by drawdowns, but seeds germinate upon
reflooding and the infestation is reborn. Drawdown will not control torpedograss, a plant that is
adapted to living in water several feet deep or in dry soils.
Advantages to drawdown are low cost; secondary benefits of sediment oxidation and consolidation and fisheries enhancement; and long term effects (two or more years). However, drawdown may reduce the diversity of desirable plant and/or fish species; may expand undesirable species, like hydrilla, into deeper areas; may produce floating islands (tussocks) upon reflooding; may affect storage water and recreational benefits of water body; may promote algal blooms due to nutrient release from sediments; and may otherwise affect fish and wildlife.A practical example of water level manipulation: Although it is diffucult, and usually impossible to completely drain most Florida lakes, and residential shoreline development precludes extreme flooding in most cases, managers use water level manipulation to enhance large-scale hydrilla control. Prior to initiating large-scale hydrilla management with fluridone herbicide, managers attempt to lower water levels by a few to several feet. This reduces the lake volume and therefore reduces the amount of herbicide used and treatment costs, sometimes by a factor of two to three times. (A six-foot reduction in the water level on 19,000-acre Lake Toho reduced application cost by nearly $6 million.) After fluridone has been in the water for 60-90 days, water levels are then increased by several feet to reduce light penetration, further stressing hydrilla and and increasing the duration of control.
Light barriers
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| Blue dye reduces light reaching plants |
Bottom Barriers
Bottom covers, or "benthic barriers", are made of growth inhibiting substances such as
sand-gravel, burlap, plastic, rubber, fiberglass screens, nylon, and other materials that prevent
rooted aquatic plants from growing. These benthic barriers typically kill plants in one to two
months and prevent new rooting colonies from becoming established. The duration of control
depends on the type of material, application technique, and sediment composition.
Nutrient Alteration
Plant growth can be affected if at least one nutrient which is required for growing is in
limited supply. Nitrogen, phosphorus, and carbon are the most common nutrients that limit plant
growth in lakes. However, unless a lake is oligotrophic, there are usually enough nutrients in the
sediment to sustain rooted plant growth. Vascular plants are limited by nitrogen and derive most
of their nutrients from the sediments rather than from the water column.
Results from nutrient alteration are very unpredictable and may actually aggravate a plant
population. For example, nutrient limitation may control planktonic algae populations and
therefore increase light penetration that will promote nuisance plant growth and expand the
population. Conversely, adding nutrients through fertilization will create an algae bloom which
will limit light penetration and will control rooted sumbersed vegetation.
Sediment (muck) removal /dredging
In extreme cases, the non-native vegetation, muck and sediments may be
entirely removed, as in the case above. Here, scraping machines and dumptrucks
remove organic sediments from Lake Jackson (Tallahassee). Hydrilla as
well as years of muck buildup from naturally decomposing plants are being taken away.
Also take a look at the muck removal project on Lake Tohopekaliga near Kissimmee on this page of this web site.
In other cases, the vegetation and the associated sediments
may be removed
by dredging machines. Dredging is expensive, creates considerable
environmental impacts, and the results are generally short lived if it is not performed deeper than
the photic, or light penetration, zone.
Advantages to benthic barriers include the ability to use the barrier at any depth (greater
than 3 feet requires the assistance of trained scuba divers), provides immediate control, high level of control, can
be installed by homeowners, are hidden from view and do not interfere with shoreline use, and
do not create plant fragments.
Yet, materials can be expensive and regular maintenance of benthic barriers is labor intensive.
The technique is generally restricted to small locations such as ornamental ponds, swimming
areas and around boat docks. Benthic barriers are not selective and plants eventually regrow after
sediments accumulate on top of the material. Benthic barriers impact bottom dwelling
organisms. Natural gases accumulate underneath the fabric and cause the barriers to
float to the surface. Small cuts is the fabric allow gas to escape and some manufacturers have
created a special fabric that prevents gas accumulation.

Chart by John D. Madsen Ph.D, University of Minnesota Used with
permission.
Email: john.madsen@mnsu.edu
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Aeration increases the dissolved oxygen in the water and can reduce plant growth, usually causing blue-green algal populations to be replaced by green algal populations. Some researchers have suggested that iron oxide compounds in aerated waters interfere with the photosynthesis of submersed plants as ochre deposits on plant parts. Others say that aeration promotes the growth of filamentous algae that interferes with photosynthesis in submersed plants. Whatever the proximate cause, aeration can be used for some degree of aquatic plant control.
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A SURPRISING VARIETY OF PHYSICAL CONTROLS are employed by aquatic plant managers throughout Florida. Although large scale physical control techniques are generally labor intensive, costly, and can produce unexpected results, simple methods such as hand-pulling and benthic barriers allow Florida homeowners to take a proactive role in invasive plant management within their own backyards.
Many parks and organizations conduct "invasive plant
roundups" and provide residents with an opportunity to work together to combat
invasive plants within their local area. However, prior to undertaking such an effort it is wise to thoroughly
understand your vegetative adversary. For example, volunteers pulled tons of hydrilla from
Wakulla Springs State Park for over a year with the result that more hydrilla existed in the
river after the project.
PREVENTION
Preventing the introduction and spread of non-native plants in Florida's waterways is the
most effective and least expensive means of restoring Florida's natural freshwater habitats.
Like all plant management techniques, physical controls can be costly and energy-intensive tools
to use in the fight to combat the non-native aquatic plant populations that are infesting Florida's
lakes, rivers and wetlands.
Time and money spent on managing invasive species can be saved in the first place by preventing
the introduction and spread of invasive species in the state's waterways. Public cooperation is an
essential part of restoring Florida's natural habitats. Please
read here about steps you can take to help prevent invasive aquatic plant problems.
This page was authored by Sarah Cervone, with assistance from Becca Hassell.
Vic Ramey is the editor.
DEP review by Jeff Schardt and Judy Ludlow.
This page is maintained by Alison Moss.
Data is from the APIRS
database.
Photography and graphics are by Ann Murray, Sara Reinhart and Vic Ramey.
CAIP-WEBSITE@ufl.edu
Copyright
2003 University of Florida