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Note: the following information was extracted from these
sources:
Aquatic Ecosystem Restoration Foundation
http://www.aquatics.org/index.html
Washington Department
of Ecology
http://www.ecy.wa.gov/programs/wq/plants/management/aqua028.html
All aquatic plant
management techniques have positive and negative attributes.
None of the techniques is without some adverse environmental
impact; all have both strengths and weaknesses. In
selecting management techniques, selections need to be based on
economic, environmental, and technical constraints.
Mechanical Harvesters
Though we have
only tried a harvester for one day in our project area, the use
of mechanical harvesters and chopping machines needs to be
carefully considered. Resulting EWM plant fragments may
easily re-grow or be carried downstream to create new
infestations; harvesting machines are effective at reducing a
large bio-mass in a short time, however, harvesting may have to
be done several times per year.
Benthic Barriers
Description of
Method
In addition to controlling nuisance weeds around docks and in
swimming beaches, benthic barriers (also bottom barriers, bottom
screening) has become an important tool to help eradicate and
contain early infestations of noxious weeds such as Eurasian
watermilfoil and Brazilian elodea. Pioneering colonies
that are too extensive to be hand pulled, can sometimes be
covered with bottom screening material.
Our barriers are made
of a 10 ft. X 10 ft. piece of spun, nylon fabric (versus woven),
attached to a square frame made of Schedule 40 PVC pipe, one (1)
inch in diameter. Opposite ends of the fabric are attached
with stainless-steel screws to two (2) straight, 10 ft. lengths
of the PVC pipe (like a scroll), which are then filled with sand
and plugged with foam. PVC elbows (90°)
are attached on each end of the two pipes, then two (2) more 10
ft. lengths of pipe are fitted into the elbows, completing the
square frame. Because the barrier can be dismantled and
rolled up, it carries well on a boat or in a truck.
Divers, once the barrier is assembled, can float over the area
of EWM infestation, then sink it into place. When removing
the barrier, it can be disassembled and rolled up, then
transferred to a waiting vehicle or boat. These barriers
are non-reactive in the water and can be reused for another
season if washed and stored dry.
The advantages of
benthic barriers is:
-
Installation
creates an immediate open area of water with no vegetation.
-
They are easily
installed around docs and in swimming areas.
-
Control of aquatic
vegetation can be up to 100%.
-
Installation can
be done (with the proper permits) by a homeowner or diver.
The disadvantages of
benthic barriers is:
-
Because they
reduce habitat by covering the sediment, they are suitable
only for localized control.
-
For safety and
performance reasons, they must be regularly inspected and
maintained.
-
Harvesters,
fishing gear, propeller backwash and boat anchors may
damage, move or dislodge the barrier.
-
If improperly
weighted or anchored, they can create a safety hazard for
boaters and swimmers.
-
Some can move if
not anchored into place on deep sediments.
-
They could
interfere with bottom-dwelling animals and fish spawning.
-
If they are not
maintained, sediment build-up will allow aquatic plants to
colonize on top of the barrier.
In Idaho, barrier
research during the 2005-2006 seasons in Lake Coeur d'Alene
showed that between 8 and 10 weeks of coverage was needed
to be effective for EWM eradication.
Permits for benthic
barriers in our area were provided by the Idaho Department of
Lands - Coeur d'Alene Field Office, limited to placement and
removal within the EWM growing season.
Costs for use of the
barriers are based on barrier materials, placement and removal.
For our projects, benthic barrier costs $1.00 per square foot,
so a standard 10 ft X 10 ft barrier placed and removed is
$100.00. A maintenance cost to clean the sediment off the
barrier during the season varies by contractor.
Diver Hand-Pulling
Description of
Method
Diver hand-pulling is
an effective way of EWM removal in small areas or for widely
scattered, single plants. When treating EWM, light to
medium infested areas within a small space can be easily removed
and the control is complete. The EWM is gently lifted from
the bottom sediment, including the root system, and placed in a
canvas or netted bag. The diver must be careful to not
damage the plants, causing fragments to form and float away.
Once the bag is full, the collected material is placed in totes
on a diving platform and disposed of at the landfill.
The advantage of
hand-pulling is:
-
Small areas can be
quickly cleaned.
-
Plants are
completely removed from the system.
-
Areas not
accessible by boat or incompatible to barrier placement can
be accessed with a diver.
-
No permits are
necessary for the work.
The disadvantages of
diver hand-pulling are:
-
The activity is
time consuming.
-
Many divers are
unfamiliar with identification of EWM.
-
The high cost per
hour or per day.
-
Disposal of the
bio-mass.
Diver hand-pulling
costs include the diver(s) labor (no less than 2 divers for
safety), air tanks and air refills or an air-assist pump, diving
platform (boat or pontoon barge), fuel, bags and totes for
disposal. The average cost is $125 per hour for two (2)
divers.
Diver Hand-Pulling/Suction Assisted
Description of
Method
Diver hand-pulling
with suction assistance (also know as diver dredging) is the
same activity as above, only instead of placing the EWM plants
in a bag, a vacuum pump and hose is utilized to suck the plants
into a catch-cage (a screen box) located on the diving platform.
Typical pumps used for the operation are dredge or mining
(reclamation) pumps, hooked up with a hose attached to a power
jet (venture tube) that creates suction as air pressure pulls
water through the hose. Divers can "vacuum" a larger area
than with hand-pulling alone, but the water can get murky with
the movement of sediment where the EWM is being pulled.
The advantages and
disadvantages are the same as hand-pulling.
Costs for diver
hand-pulling with suction assistance are slightly higher than
hand-pulling alone, due to the added expense of the pump system
being part of the equipment necessary for the job. The
average cost is $240 per hour for two (2) divers.
Herbicides
Description of
Method
Aquatic herbicides are
chemicals which are specifically formulated for use in water to
kill or control aquatic plants. Herbicides approved for
aquatic use by the United States Environmental Protection Agency
(EPA) have been studied and tested and are considered compatible
with the aquatic environment when used according to label
directions. Aquatic herbicides can be sprayed directly
onto floating or emergent aquatic plants or applied to the water
in either a liquid or pellet/granular form. Liquid
herbicides are generally injected below the water surface while
the pellet/granular forms are spread across the water surface
and allowed to sink. Systemic herbicides are
capable of killing the entire plant. Contact herbicides
cause the parts of the plant in contact with the herbicide to
die back, leaving the roots alive and able to regrow.
Non-selective, or "broad spectrum" herbicides will generally
affect all plants that they come in contact with.
Selective herbicides will affect only some plants. Often
dicots - broad leafed plants like Eurasian watermilfoil (Myriophyllum
spicatum) - will be affected by selective herbicides whereas
monocots like most native aquatic plants will not.
Because of
environmental risks from improper application, aquatic herbicide
application in Idaho waters is regulated and has the following
restrictions:
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Applicators must
be licensed by the Idaho Department of Agriculture.
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Notification to
appropriate State or Tribal agencies is required before
applications are made.
-
Notification and
posting are required and there may be additional mitigations
proposed to protect rare plants or threatened and endangered
species.
The chemicals that are
currently permitted for use in controlling EWM in Idaho are:
Fluridone –
(Trade names for fluridone products include: Sonar® and
Avast!®). Fluridone is a slow-acting systemic herbicide used
to control Eurasian watermilfoil and other underwater
plants. It may be applied as a pellet or as a liquid.
Fluridone can show good control of submersed plants where
there is little water movement and an extended time for the
treatment. Its use is most applicable to whole-lake or
isolated bay treatments where dilution can be minimized.
Fluridone is generally not effective for spot treatments of
areas less than five acres. It is slow-acting and may take
six to twelve weeks before the dying plants fall to the
sediment and decompose. When used to manage Eurasian
watermilfoil, fluridone is applied several times during the
spring/summer to maintain a low, but consistent
concentration in the water. Some new granular formulations
of fluridone are proving to be effective when treating areas
of higher water exchange. Although fluridone is considered
to be a broad spectrum herbicide, when used at very low
concentrations, it can be used to selectively remove
Eurasian watermilfoil. Some native aquatic plants,
especially pondweeds, are minimally affected by low
concentrations of fluridone.
(Click here to read product label for Sonar AS liquid)
(Click here to read product label for Sonar PR pellet)
2,4-D – There
are two formulations of 2,4-D approved for aquatic use. The
granular formulation contains the low-volatile butoxy-ethyl-ester
formulation of 2,4-D (Trade names include: AquaKleen® and
Navigate®). The liquid formulation contains the
dimethylamine salt of 2,4-D (Trade name - DMA*4IVM). 2,4-D
is a relatively fast-acting, systemic, selective herbicide
used for the control of Eurasian watermilfoil and other
broad-leaved species. Both the granular and liquid
formulations can be effective for spot treatment of Eurasian
watermilfoil. 2,4-D has been shown to be selective to
Eurasian watermilfoil when used at the labeled rate, leaving
native aquatic species relatively unaffected. (Click
here to read Washington’s 2,4-D risk assessment)
(Click here to read product label for DMA 4 IVM)
(Click here to read product label for Navigate).
Triclopyr -
(Trade name Renovate3®). There are two formulations of
triclopyr. It is the TEA formation of triclopyr that is
registered for use in aquatic or riparian environments.
Triclopyr, applied as a liquid, is a relatively fast-acting,
systemic, selective herbicide used for the control of
Eurasian watermilfoil and other broad-leaved species such as
purple loosestrife. Triclopyr can be effective for spot
treatment of Eurasian watermilfoil and is relatively
selective to Eurasian watermilfoil when used at the labeled
rate. Many native aquatic species are unaffected by
triclopyr. (Click
here to read Washington's Environmental Impact Statement for
triclopyr)
(Click here to read product label for Renovate 3 liquid)
(Click here to read product label for Renovate OTF flake).
Endothall –
(Trade name Aquathol®) Endothall, the dipotassium salt, is a
fast-acting non-selective contact herbicide which destroys
the vegetative part of the plant but generally does not kill
the roots. Endothall may be applied in a granular or liquid
form. Typically endothall compounds are used primarily for
short term (one season) control of a variety of aquatic
plants. However, there has been some recent research that
indicates that when used in low concentrations, endothall
can be used to selectively remove exotic weeds; leaving some
native species unaffected. Because it is fast acting,
endothall can be used to treat smaller areas effectively.
Endothall is not effective in controlling Canadian waterweed
(Elodea canadensis) or Brazilian elodea. (Click
here to read Washington’s risk assessment for endothall)
(Click here to read product label for Aquathol K liquid)
(Click here to read product label for Aquathol Super K
granular).
Diquat –
(Trade name Reward®). Diquat is a fast-acting non-selective
contact herbicide which destroys the vegetative part of the
plant but does not kill the roots. It is applied as a
liquid. Typically diquat is used primarily for short term
(one season) control of a variety of submersed aquatic
plants. It is very fast-acting and is suitable for spot
treatment. However, turbid water or dense algal blooms can
interfere with its effectiveness. (Click
here to read Washington’s risk assessment for Diquat)
(Click here to read product label for Reward).
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