
Eurasian watermilfoil is a perennial,
submersed aquatic plant that is native to Europe, Asia and Africa. It is believed to have
become established in north America in the l940s and has quickly spread across the
continent and is found in most U.S. states and Canadian Provinces. Eurasian watermilfoil
is capable of growth in a wide range of habitats (lake types) and spreads from lake to
lake as plant fragments; boats and waterfowl are the most likely vector of dissemination.
Habitat Preference and
Characteristics
Eurasian watermilfoil is commonly found on
soft organic sediments but will colonize rocky and sandy substrates as well. It is capable
of growing aerially in times of low water and in depths of more than 7 meters. It appears
to be capable of growing in deeper waters and to be more shade tolerant than most native
plant species. These characteristics, shade tolerance and the ability of this plant to
grow in deep water, have assisted Eurasian watermilfoil in what has become its typical
invasion pattern. Eurasian watermilfoil will generally colonize the deeper water where
native vegetation is absent. It then displaces the native plants of the shallower waters
by creating a canopy over the adjacent plants, shading and crowding them out. Eurasian
watermilfoil is opportunistic and extremely aggressive. It is commonly found growing in
areas that are not highly disturbed but seems to reach nuisance production levels more
rapidly in disturbed areas created by inappropriately applied lake management strategies.
These strategies include mechanical harvesting, recreational uses and other anthropogenic
(human induced) ecosystems disturbances, such as accelerated sediment
loading as a result of development and agriculture. It consistently demonstrates an
ability to grow earlier and much faster than competing native plants in such disturbed
areas.
Reproductive and Dispersal
Characteristics
Eurasian watermilfoil is commonly known to
crowd out native aquatic plant species. The reproductive characteristics and
over-wintering habits help to ensure its predominance over more desirable native North
American submersed plants. It over-winters a considerable amount of evergreen type
biomass, providing this exotic with a formidable competitive advantage over many native
plant species. By over-wintering biomass, it can hold growing space at the beginning of
the growing season limiting native growth.
Eurasian watermilfoil is capable of explosive
growth at the very beginning of the growing season, which provides it with another
competitive advantage over native plants. Native plants typically begin growth later in
the year.
Most experts agree that vegetative spread is
its chief form of dispersal. A fragment, including a single node, is capable of
producing a new plant, and any mechanical disturbances of this plant (i.e. boat motors,
aquatic plant harvesting, etc.) will dramatically enhance its dispersal and dominance of
native lake flora. Plant fragments are also known to withstand the rigors of desiccation,
as might be encountered on a boat motor or trailer as it is transported from lake to lake.
Eurasian watermilfoil will also spread by
means of stolons, which are specialized stems that "creep" over the bottom of
the lake. This type of spread is commonly observed in the autumn through the early summer
of each proceeding season.
Some Specific Impacts caused by
Eurasian watermilfoil
1. Native
plant beds provide twice as many invertebrates per square meter than Eurasian watermilfoil
beds (Keast, 1983).
2. As
Eurasian watermilfoil density increases, native plant diversity decreases. (Trebitz,
1993).
3. As
plant densities increase beyond a certain threshold, water movement within the Milfoil bed
is severely restricted and reduced light levels result in a curtailment of photosynthetic
production oxygen. (Lillie & Budd, 1992).
4. Reduced
levels of dissolved oxygen, the release or build up of nutrients, and other changes in
water chemistry may provide unfavorable conditions for both micro invertebrates and fish.
(Lillie & Budd, 1992).
5. Three
to four times the number of fish was observed in native plant beds versus Eurasian
watermilfoil beds. (Keast, 1993).
Management Strategies of Eurasian watermilfoil
Mechanical harvesting is not recommended for control of Eurasian watermilfoil
for two reasons.
1.
The potential for plant fragmentation by
mechanical harvesters can serve to spread Eurasian watermilfoil beyond the management
area(s) and intensify problems throughout an infested lake.
2.
Eurasian watermilfoil will usually dominate
the re-growth community and gain further advantages over native plant species because of
its faster relative growth rate.
The
use of selective, systemic aquatic herbicides has proven to be the best management tool to
control Eurasian watermilfoil to date. 2,4-D and fluridone products have been the two top
choices in this chemical category.
2,4-D has been used extensively for the
management of Eurasian watermilfoil in many lakes and ponds for many years with a great
deal of success. 2,4-D can also be used as a spot-treatment tool and has
repeatedly been proven to be highly selective against Eurasian watermilfoil when used at a
narrow range of application rates. Nearly all of the native submersed plant species are
unaffected by 2,4-D when used at the rates required for the management of Eurasian
watermilfoil.
Fluridone is highly mobile in surface water
and therefore must be applied to achieve a volume or a targeted concentration throughout
the entire lake. Fluridone is not commonly used as a -spot-treatment" herbicide.
Unlike most aquatic herbicides, low water temperatures do not compromise the efficacy of
fluridone. These three characteristics, Eurasian watermilfoil sensitivity, temperature
tolerance and the early production of Eurasian watermilfoil along with the solubility of
formulations and the systemic activity of this herbicide make fluridone another viable
choice for the renovation and restoration of submersed flora communities.
