PHYSICAL CONTROL

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 |

using rakes is physical control

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".

manual removal of aquatic plants


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.

diver-assisted dredging

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.

hydrilla drawdown hydrilla drawdown water lettuce exposed to freeze dessicated water lettuce drawdowns compact sediments dry lake bottom

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

AQUASHADE dye dispersing into the water
Blue dye reduces light reaching plants
Light reduction, or attenuation, limits plant growth by reducing light penetration into the water and inhibiting photosynthesis. Sunlight is obstructed by special non-toxic dyes or shade-making structures that are placed along the shoreline. Light barriers are most useful in small ponds that are greater than 3 feet deep.


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.

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.


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.


scraping muck during drawdown is this physical or mechanical control?

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.


CHARACTERISTICS OF PHYSICAL MANAGEMENT TECHNIQUES
Chart by John D. Madsen Ph.D, University of Minnesota Used with permission.
Email: john.madsen@mnsu.edu

Management Method

Description

Advantages

Disadvantages

Systems where used effectively

Plant species response

Dredging / Sediment Removal

Use mechanical sediment dredge to remove sediments, deepen water

Creates deeper water, very long-term results

Very expensive, must deal with dredge sediment

Shallow ponds and lakes, particularly those filled in by sedimentation

Often creates large usable areas of lake, not selective

Drawdown

"De-water" a lake or river for an extended period of time

Inexpensive, very effective, moderate-term

Can have severe environmental impacts, severe recreational/riparian user effects

Only useful for manmade lakes or regulated rivers with a dam or water control structure

Selective based on perennation strategy; effective on evergreen perennials, less effective on herbaceous perennials

Benthic Barrier

Use natural or synthetic materials to cover plants

Direct and effective, may last several seasons

Expensive and small-scale, nonselective, barriers float to surface-must be anchored

Around docks, boat launches, swimming areas, and other small, intensive use areas

Nonselective, plant mortality within one month underneath barrier

Shading / Light Attenuation

Reduce light levels by one of several means: dyes, shade cloth, plant trees (rivers)

Generally inexpensive, effective

Nonselective, controls all plants, may not be aesthetically pleasing

Smaller ponds, man-made waterbodies, small streams

Nonselective, but may be long-term

Nutrient Inactiviation

Inactivate phosphorus (in particular) using alum

Theoretically possible

Impractical for rooted plants limited by nitrogen

Most useful for controlling phytoplankton by inactivating water column P

Variable


Fire

results of fire may last years
controlling torpedo grass with fire
The suppression of natural fires has altered historical plant communities and aided fire-intolerant invasive species such as torpedograss, Panicum repens. Plant managers use prescribed fires to suppress plant growth and kill plants that are not fire tolerant. The effect of a single burn is unpredictable, but the results may last for several years. The success of fire is dependent on the intensity of fire, the time of year, and the targeted plant species. Plant managers must consider the effects on soil loss and water quality and impacts on humans and wildlife.


an aerator another aerator and another aerator
Aeration

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.


airboats herding water hyacinths

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.


The Creators

This page was authored by Sarah Cervone, with assistance from Becca Hassell.
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.

Vic Ramey is the editor.

DEP review by Jeff Schardt and Judy Ludlow.

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A collaboration of the Center for Aquatic and Invasive Plants, University of Florida, and the Invasive Plant Management Section of the Florida Fish and Wildlife Conservation Commission.


CAIP-WEBSITE@ufl.edu
Copyright 2003 University of Florida