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Muskrats To Lead Charge in Eradicating Zebra Mussels in Cazenovia Lake? Recently the Lake Association recieved this letter from a Cazenovia Lake Resident.
Could the Lake Assoc adopt the muskrat as out mascot?' The following research was done by joint effort on the part of several Cazenovia Lake Association Members.
muskrat. [Photograph]. Retrieved December 14, 2007, from |
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Reprinted from Journal of Freshwater Ecology (2003) 18(1): 25-32 with kind permission from Oikos
Muskrat (Ondatra zibethicus) Predation on Zebra Mussels (Dreissena polymorpha) Attached to Unionid Bivalves Muskrats (Ondatra zibethicus) commonly prey upon unionid bivalves, discarding the empty shells in discrete piles or middens. We found large numbers of live unionids and the shell remains of zebra mussels (Dreissena polymorpha) in muskrat middens on the upper Ohio River and upper Mississippi River. Muskrats apparently began preying on zebra mussels that were attached to unionids following an increase in zebra mussel abundance at the study sites. Significantly fewer zebra mussels were attached to live unionids at muskrat middens than to ones collected from reference sites away from middens. We also found a group of stones with numerous zebra mussel byssal threads at an Ohio River midden, suggesting muskrats retrieved and ate the attached zebra mussels. We view this, as well as the fact that muskrats discarded live unionids, as evidence that muskrats were selectively preying on zebra mussels rather than unionids. Contact: John Tucker, Long Term Resource Monitoring Program Pool 26, Illinois Natural History Survey, 4134 Alby Street, Alton, IL 62002, USA |
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Reprinted from American Zoologist 36:300-310 (1996)
Zebra Mussel Infestation of Unionid Bivalves (Unionidae) in North America SYNOPSIS In 1989, zebra mussels received national attention in North America when they reached densities exceeding 750,000/m 2 in a water withdrawal facility along the shore of western Lake Erie of the Laurentian Great Lakes. Although water withdrawal problems caused by zebra mussels have been of immediate concern, ecological impacts attributed to mussels are likely to be the more important long-term issue for surface waters in North America. To date, the epizoic colonization (i.e., infestation) of unionid bivalve mollusks by zebra mussels has caused the most direct and severe ecological impact. Infestation of and resulting impacts caused by zebra mussels on unionids in the Great Lakes began in 1988. By 1990, mortality of unionids was occurring at some locations; by 1991, extant populations of unionids in western Lake Erie were nearly extirpated; by 1992, unionid populations in the southern half of Lake St. Clair were extirpated; by 1993, unionids in widely separated geographic areas of the Great Lakes and the Mississippi River showed high mortality due to mussel infestation. All infested unionid species in the Great Lakes (23) have become infested and exhibited mortality within two to four years after heavy infestation began. Data indicate that mean zebra mussel densities >5,000-6,000/m 2 and infestation intensities >100-200/unionid in the presence of heavy zebra mussel recruitment results in near total mortality of unionids. At present, all unionid species in rivers, streams, and lakes that sympatrically occur with zebra mussels have been infested and, in many locations, negatively impacted by zebra mussels. We do not know the potential consequences of infestation on the 297 unionid species found in North America, but believe zebra mussels pose an immediate threat to the abundance and diversity of unionids. Contact: D.W. Schloesser, National Biological Service, Great Lakes Science Center, Ann Arbor, Michigan 48105 |
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Reprinted from U.S. Army Corps of Engineers (USACE)
Zebra Mussel Impacts on Unionids
Unionid after zebra mussel removal.
From European studies it is known that the extensive overgrowth by Dreissena of unionids, resulting in mass mortality, is characteristic of periods of rapid population growth of zebra mussels when they invade a new water body (Sebestyen 1937, Dussart 1966, Karatayev and Burlakova 1995a). Following this period, Dreissena tend |
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