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GLWMO MINUTES <br />JANUARY 24, 2008 <br />PAGE 7 <br />Mr. Sobiech stated that the macrophyte survey showed a high density of curly leaf <br />pondweed. This finding agrees with what lake management is seeing at the southern end <br />of the lake and is the reason for the increase in phosphorous. It is impacting the water <br />quality in the lake. <br />The sediment core analysis shows the potential for Lake Owasso to have phosphorous <br />from bottom sediments as low compared to other metro area lakes. <br />Stark noted that there seems to be correspondence between the rates and deeper parts <br />having more mobile phosphorous. Sobiech responded that in 2002, the MPCA completed <br />a diatom study of 55 Minnesota lakes, including Lake Owasso. This study shows that <br />historically the phosphorous content was 10 and 25 micrograms per liter, which is <br />significantly better than where it is now. Last summer it was 33 and 31 micrograms per <br />liter. It is safe to say the natural watershed at its best could expect approximately 20 <br />micrograms per liter. <br />Ferrington asked if there will be a raw data diatom report. Mr. Sobiech answered that the <br />MPCA report can be made available to the Board. <br />Stark asked if the MPCA diatom report fits the state's regional standards for <br />phosphorous. Mr. Sobiech stated that the analysis shows that the area of development <br />near the lake averages a concentration of 40 micrograms per liter with a range of 25 to <br />55. The data collected in this study agrees with that analysis. <br />The actual watershed models the P8 computer program. Table 3 summarizes the total <br />measured versus predicted pollutant loads for all events at each of the monitoring sites. <br />Referring to footnote a of Table 3, during the entire summer of 2007, there were five <br />events where enough data was collected to calibrate. The better site was West Owasso <br />Boulevard which had eight storm events to calibrate. The first thing to look at in the <br />models is to produce the right volume of runoff coming from the watershed which is <br />compared to the monitoring data. Over time all three station models did well estimating <br />volumes of runoff. The site used for Table 3 to estimate pollutants has not pond. That <br />allowed calibration of the watershed parameters and not worry about treatment by BMP. <br />From that calibration at that site, an estimate of depression storage was calculated to see <br />how much water sits before runoff occurs. The other two locations indicated a pond <br />infiltration rate. A lot of pond water levels are low. Infiltration and evaporation are <br />occurring. Water levels have to fill before it gets to the lake. <br />The outlet from Lake Owasso freezes during the winter, which is why the lake level stays <br />above normal in winter. <br />