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• <br /> The inorganic nitrogen concentrations (NO3-N + NH4-N) in the surface <br /> waters during the summer varied between 30 and 120 ugil with lowest <br /> concentrations occurring during mid-June and late August in 1976. These <br /> concentrations should not produce excessive algae blooms during the <br /> summer months. However, spring concentrations of total phosphorus are <br /> quite high and are indicative of eutrophic conditions. <br /> The chlorophyll a concentrations throughout the summer months were low <br /> (Figure B-22) , with correspondingly good water transparency. No <br /> algae blooms occurred at the surface during summer months. Stauffer <br /> (1974) monitored Fish Lake in 1972 and provided data indicating similar <br /> low surface chlorophyll concentrations, but also a summer chlorophyll <br /> maximum of about 20 ugh occurring at about 10 meters in depth. This <br /> condition is often the result of Oscillatoria rubescens, a cold-water <br /> blue-green filamentous algae that is found near the lake surface <br /> during spring and fall and in the lower metalimnion during the summer, <br /> if light penetration is sufficient through the epilimnion. Oscillatoria <br /> sp. was confirmed in the surface plankton of Fish Lake during the spring <br /> and fall of 1976 and 1977, when chlorophyll concentrations were rela- <br /> tively high, but not during the summer months when chlorophyll concen- <br /> trations were low. This may explain the relatively high concentrations <br /> of total phosphorus found during spring turnover which did not result in <br /> any excessive summer phytoplankton growth in surface waters. <br /> A comparison between the phosphorus data collected by Stauffer (1974) <br /> in 1972 and the monitoring data collected in 1976 and 1977 indicated an <br /> increase in summer concentrations of total phosphorus in both the <br /> epilimnion and hypolimnion. All of the 1972 data had surface concentra- <br /> tions of total phosphorus no greater than 20 ug/1 whereas the 1976 and <br /> 1977 monitoring data had concentrations ranging between 20 and 50 u9/1 <br /> as previously mentioned. Although Stauffer did not always sample at <br /> the deepest location in the lake, generally his hypolimnetic phosphorus <br /> concentrations were less than 60 ugh] throughout the entire summer period, <br /> even though his dissolved oxygen concentrations were near extinction. <br /> The 1976 and 1977 monitoring data indicated hypolimnetic phosphorus <br /> concentrations to be as much as 200 ug/1 or higher. High concentrations <br /> of phosphorus in the hypolimnion are the result of phosphorus (dissolved <br /> reactive) coming into solution from anaerobic lake sediments rich in <br /> phosphorus . <br /> The concentrations of phosphorus in Fish Lake during 1976 and 1977 were <br /> not as high as concentrations found in other eutrophic lakes, or lakes <br /> Mendota or Monona, but are sufficiently higher than the 1972 data to <br /> warrant concern about the increase in phosphorus availability within <br /> Fish Lake. A detailed study should be initiated on Fish Lake to assess <br /> the role of the mobile home park septic systems on this apparent increase <br /> in lake phosphorus concentrations. Fish Lake has the best water quality <br /> of any lake in Dane County, and therefore, prevention of any further <br /> degradation is warranted. Fish Lake has the potential to support some <br /> cold-water fish such as cisco; however, pollutants must be reduced and <br /> summer dissolved oxygen conditions must be improved if the lake is to <br /> continue to support any cold-water fish. <br /> B-103 <br />