Consultant's Report - Minnesota State Legislature
Consultant's Report - Minnesota State Legislature
Consultant's Report - Minnesota State Legislature
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MINNESOTA DEPARTMENT OF NATURAL RESOURCES<br />
Feasibility Study to Limit the Spread ofZebra Mussels from Ossawinnamakee Lake<br />
implement a vibration system in either the brook or the lake because there are few structures that<br />
can be subjected to vibration.<br />
Overall, acoustic deterrent systems have relatively high capital costs and may be feasible for<br />
certain areas in Ossawinnamakee Lake, but efficiencies ofthese systems have not been proven in<br />
open water settings. In fact, research pertaining to acoustic deterrents for control of zebra<br />
mussels in water intakes was documented as long as thirty years ago primarily for intakes, but<br />
there are no cases to our knowledge of acoustic systems that have been implemented in open<br />
water systems.<br />
Chemical Controls<br />
Chemical treatments have some advantages over the other treatment alternatives because they<br />
have high efficiencies and are relatively easy to implement within open water systems such as<br />
the lake and/or brook. Specifically, Muskie Bay could be utilized as a potential treatment area<br />
and the brook may benefit from residual chemical levels, as exhibited by the current treatment.<br />
Capital costs for chemical treatments are generally reduced due to the limited equipment needed<br />
to implement chemical dosing; however, operational and maintenance costs (i.e., man hours and<br />
chemicals) may be higher than some other treatment alternatives. Overall, the major<br />
disadvantages for chemical treatments include environmental impacts to non-target organisms<br />
and health and safety of the operators that handle the chemicals. With these considerations in<br />
mind, a brief statement is provided (within the subdivided categories) to explain why or why not<br />
each chemical would be advantageous for zebra mussel control in the lake and/or the brook.<br />
Aside from toxicology, chemical treatments are a viable option for implementation in Muskie<br />
Bay or Pelican Brook, although implementation may be more difficult in the brook due to higher<br />
flows.<br />
Oxidizing Agents<br />
The oxidizing chemicals discussed in Section V are generally effective in reducing zebra mussel<br />
populations; however, this class of chemicals is best suited for application within controlled,<br />
closed water systems. The use of oxidizing chemicals in natural, open water systems is limited<br />
due to toxicity and impacts to non-target organisms, potential occupational safety issues, and the<br />
regulatory permitting issues/restrictions. In addition, there could potentially be higher<br />
operational costs (in comparison to non-oxidizing agents) associated with administration of<br />
oxidizing agents because juvenile and adult zebra mussels can detect chemical oxidants and<br />
subsequently close their shells to protect themselves from the harsh environment.<br />
Toxicity is a major disadvantage to several of these chemicals. Chlorine is harmful to the<br />
environment due to release of trihalomethanes and it is toxic to many species other than zebra<br />
mussels. Hydrogen peroxide is not advantageous because it must be utilized at a high<br />
concentration to produce mortality and it is also toxic to native mussels species. Potassium<br />
permanganate is not advantageous because it must be continuously administered in order to<br />
VI-5 Alternatives Analysis and Recommendations