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September 19, 2011 <br />TO: Members of the GLWMO Board of Commissioners <br />FROM: Tom Petersen <br />Administrator <br />SUBJECT: Highlights/Paraphrase summary of the April, 2009 Barr Lake Owasso <br />Use Attainability Analysis Report <br />Overview: <br />Study provides the scientific foundation for a lake specific management plan. Study <br />completed in 2007 and 2008. Very dry years. Additional stormwater monitoring <br />completed in 2009. Citizens have concerns about excessive macrophytes that competes <br />with recreational uses and decreasing lake clarity. <br />Conclusions: <br />• Water quality data from 2007 & 2008 would classify Owasso as an Eutrophic <br />Lake. <br />• Data from 1998 to 2008 shows decrease in Secchi Disk with little change in <br />Phosphorous and increase Chlorophyll a. <br />• Owasso's water quality falls within expected range for a minimally- impacted lake <br />with similar characteristics and shows potential for water quality improvement. <br />• There is internal loading within Owasso but may be significantly less than the <br />average observed across the Metro area. <br />• May 2007 survey shows Curlyleaf pondweed on 52% of the Lake and can act as a <br />significant source of phosphorous (2010 study which was conducted after the <br />LOA sprayed for vegetation showed Curlyleaf pondweed on 17% of Lake). <br />• Evidence suggests the lake stratifies in the summer. <br />• It is possible for mixing to occur in shallow areas of the Lake as the result of wind <br />and motor boat activity although it is unclear what role mixing has on the overall <br />water quality of the Lake. Anecdotal information suggests that turbidity in the <br />Lake increases as the result of motor boats in shallow areas of the Lake. <br />• Carp may be a problem in the Lake resulting in internal phosphorous release and <br />loading. <br />• Watershed runoff plays a variable roll in total phosphorous loads to the Lake <br />depending on climatic conditions ranging from 12 to 23% of the total load. <br />• Internal phosphorous loads from within the Lake (the result of Curlyleaf <br />Pondweed die -back, release from Lake sediments, wind mixing, and rough fish <br />activity were estimated to range from 50 to 57% of the Load to the Lake. Other <br />sources include atmospheric deposition and groundwater. <br />• In Lake Monitor modeling indicates that control of Curlyleaf Pondweed will have <br />the most significant impact on total phosphorous concentrations. <br />