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Laske Owasso Task Force
Roseville
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1996 Lake Owasso Task Force
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Laske Owasso Task Force
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Lake Uwasso Task Force <br />Summ�ry of Discussion with the Environmental Panel (12/18/96) <br />Panel Member; Ed Musielewi2c-Natural Resources Consen�ation Service <br />Tecz,y Noonar�-Ramsey Counry Public Works Deparnnent <br />Tom Aeterson Ramsey County Soil and Water C'onservation District <br />Joel Sehillin�z-5hort Eiliot and Hendrickson, fnc. <br />Uave 7t�petillo-DNR Fislieries <br />Weeds and algae: Aquatic ve�etation is a probletn in Lake Owasso, but less a problem than in marry <br />local lakes. About 24�31 % of the lake haS ahundant plant growth in summer. Aquatic plants provide fish <br />habitat, hut are a problem for boaters and swim�ners. DNR treats 2$�io of Lal:e Owasso's littoral zone <br />with herhicides. F�erbicides are appHeci f'rom May to Jul,y. 7'his is more that the 1�% of' a lake's are�d <br />allowed to bc treated but is allowed because of a�•andfather clause. Aquat.ic plants and algae require <br />nutncnts for �owth. Nutrients can come from internal (lake) or external (watershed) so�uces. The <br />relative importance �f these sources for the lake is not precisely known, but interna] sources appear to be a <br />signiticant source of nutrients to the lake. August aigae blooms result frum v��ann water and the release of <br />nutriettts from decaying plants in the lal:e, <br />Fish habitat. The lalce is mana�ed by the DNR %r walleye and mnskie. 'Che lal:e is below the average, <br />in terms of tish �rc�duetivity, relaiive t� si�nilar lakes, Fish in the lalce are fienerally not impacted. by the <br />lake's turbidity (sus�ended solids and algae}, except in the sprin�„ At these tiines turbidity and hoat traf�c <br />disturb spawning. <br />Em�ironmental impaet of b�ating: Boating has the potential to scour bottom sediments , resuspend <br />bottorn sediments, and destroy near-shc►rc ro�ted plants that protect shorelines from erosi�n. These <br />impacts are most si�;nificant in shallow water (less than six feet or s�j. Tl�e potential impact of reducing <br />the no-wal:e zone on lake quality is unclear, although morc bc�ats traveling cl�ser to the shore in shall.ow <br />areds of'the lake; was censidered to be a negative factor in tenns of the ecologica.l health of the lake, <br />Elow hag the qualtiy of the lake chan�ed over time: The MPCA has su�;�ested th�ti t�►e clariry of <br />the lake has improved, on an annual basis. This improvement is less clear statistically when data fron� <br />oniv the summer months are examine�i. Wced harvesting, herbicide application, and bnating seem to be <br />signific:ant in reducing the amount of rooted weeds in the lake, hut do n�t improve algae �r turbidity <br />prublems in the lake. The turbsdiry of the iake is hi�her that in other similar lakes. Internal a�id external <br />loadinKs of' nutrients and seditncnt are a significant problem. Excessive boating may result in fewer <br />rooted aquatic plants, but in and increase in al.gae and in turbidity. Turbidity is also dependent on the depth <br />and sha}�e of the lake and on local w�ind conditions. The relative contributions o�'these factot's is difficult <br />to quantify. Excessive wave action, from winds nr boats, are also responsible for shoreline erosion and a <br />potential f'or an increase in lake turbidity. <br />
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