The
milfoil weevil photograph used with permission - Dr. Ray Newman
The Milfoil Weevil in Washington
The milfoil weevil, Euhrychiopsis lecontei, has been associated
with declines of Eurasian watermilfoil (Myriophyllum spicatum) in
the United States (e.g. Illinois, Minnesota, Vermont, and Wisconsin).
Researchers in Vermont found that the milfoil weevil can negatively impact
Eurasian watermilfoil by suppressing the plants growth and reducing its
buoyancy (Creed and Sheldon 1995). In 1989, state biologists reported that
Eurasian watermilfoil in Brownington Pond, Vermont had declined from
approximately 10 hectares (in 1986) to less than 0.5 hectares. Researchers
from Middlebury College, Vermont hypothesized that the milfoil weevil,
which was present in Brownington Pond, played a role in reducing Eurasian
watermilfoil (Creed and Sheldon 1995). During 1990 through 1992,
researchers monitored the populations of Eurasian watermilfoil and the
milfoil weevil in Brownington Pond. They found that by 1991 Eurasian
watermilfoil cover had increased to approximately 2.5 hectares
(approximately 55-65 g/m2) and then decreased to about 1
hectare (<15 g/m2) in 1992. Weevil abundance began
increasing in 1990 and peaked in June of 1992, where 3 - 4 weevils (adults
and larvae) per stem were detected (Creed and Sheldon 1995). These results
supported the hypothesis that the milfoil weevil played a role in reducing
Eurasian watermilfoil in Brownington Pond.
Another documented example where a crash of Eurasian watermilfoil has
been attributed to the milfoil weevil is in Cenaiko Lake, Minnesota.
Researchers from the University of Minnesota reported a decline in the
density of Eurasian watermilfoil from 123 g/m2 in July of 1996
to 14 g/m2 in September of 1996. Eurasian watermilfoil remained
below 5 g/m2 in 1997, then increased to 44 g/m2 in
June and July of 1998 and declined again to 12 g/m2 in
September of 1998 (Newman and Biesboer, in press). In contrast,
researchers found that weevil abundance in Cenaiko Lake was 1.6 weevils
(adults and larvae) per stem in July of 1996. Weevil abundance, however,
decreased with declining densities of Eurasian watermilfoil in 1996 and by
September 1997 weevils were undetectable. In September of 1998 weevil
abundance had increased to >2 weevils per stem (Newman and Biesboer, in
press).
Based on observations made by researchers in Vermont, Ohio and
Wisconsin it seems that having 2 weevils (or more) per stem is adequate to
control Eurasian watermilfoil. However, as indicated by the study
conducted in Cenaiko Lake, Minnesota, an abundance of 1.5 weevils per stem
may be sufficient in some cases (Newman and Biesboer, in press).
In Washington State, the milfoil weevil is present primarily in eastern
Washington and occurs on both Eurasian and northern watermilfoil (M.
sibiricum), the
latter plant being native to the state (Tamayo et. al.
1999). During the summer of 1999, researchers from the University of
Washington determined the abundance of the milfoil weevil in 11 lakes in
Washington. They found, that weevil abundance ranged from undetectable
levels to 0.3 weevils (adults and larvae) per stem. Fan Lake, Pend Oreille
County had the greatest density per stem
or 0.6 weevils (adults, larvae and eggs per stem). The weevils were
present on northern watermilfoil. These abundance results are well below
the recommendations made by other researchers in Minnesota, Ohio, Vermont,
and Wisconsin of having at least 1.5 - 2.0 weevils per stem in order to
control Eurasian watermilfoil. The photograph of a milfoil weevil egg
is used with the permission of L. Jester.
To date, there have not been any documented declines of Eurasian
watermilfoil in Washington State that can be attributed to the milfoil
weevil, although Creed speculated that declines of Eurasian watermilfoil
in Lake Osoyoos and the Okanogan River may have been caused by the milfoil
weevil. In Minnesota, Cenaiko Lake is the only lake in that state that has
had a Eurasian watermilfoil crash due to the weevil; other weevil lakes
are yet to show declines in Eurasian watermilfoil.
Researchers in Minnesota have suggested that sunfish predation may be
limiting weevil densities in some lakes (Sutter and Newman 1997). The
latter may be true for Washington State as sunfish populations are present
in many lakes in the state, including those with weevils. In addition,
other environmental factors that may be keeping weevil populations in
check in Washington, but have yet to be studied, include over-wintering
survival and habitat quality and quantity (Jester et. al. 1997; Tamayo et.
al., in press). Although the milfoil weevil shows potential as a
biological control for Eurasian watermilfoil more work is needed to
determine which factors limit weevil densities and what lakes are suitable
candidates for weevil treatments in order to implement a cost and control
effective program.
Literature Cited
Creed, R. P., and S. P. Sheldon. 1995. Weevils and watermilfoil: did a
North American herbivore cause the decline of an exotic plant? Ecol.
Applic. 5:1113-1121.
Jester, L. L., M. A. Bozek, S. P. Sheldon, and D. R. Helsel. 1997. New
records for Euhrychiopsis lecontei (Coleoptera: Curculionidae) and
their densities in Wisconsin lakes. Gr. Lakes Entomol. 30: 169-176.
Newman, R. M., and D. D. Biesboer. A decline of Eurasian watermilfoil
in Minnesota associated with the milfoil weevil, Euhrychiopsis lecontei.
J. Aquat, Plant Manage. In Press.
Sutter, T. J., and R. M. Newman. 1997. Is predation by sunfish (Lepomis
spp.) an important source of mortality for the Eurasian watermilfoil
biocontrol agent Euhrychiopsis lecontei? J. Freshwat. Ecol.
12:225-234.
Tamayo, M., C. W. O’Brien, R. P. Creed, C. E. Grue, and K. Hamel.
1999. Distribution and classification of aquatic weevils (Coleoptera:
Curculionidae) in the genus Euhrychiopsis in Washington State.
Entomol. News 110:103-112.
Tamayo, M., C. E. Grue, and K. Hamel. The relationship between water
quality, watermilfol frequency, and weevil distribution in the State of
Washington. J. Aquat. Plant Manage. In Press.
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