Controlling Cyanobacteria in a Eutrophic Water Supply
| Cyanobacteria / blue green algae was controlled in a eutrophic water supply using a reservoir diffused aeration destratification system. The following article describes how eutrophication was corrected to rid the water supply of geosmin caused by cyanobacteria in the drinking water.
Summary of the Feng-Shan Reservoir Project: Robert L. Laing, and Carlton J. Rausch, CLEAN-FLO International
Background: Oxygen just below the surface to the bottom was 0.0 mg/l. Ammonia averaged 1.8 mg/l for five years before the project began, and had a maximum value of 3.6 mg/l. The Taiwan government wanted to rid the drinking water of the bad taste and odor. To accomplish this goal, CLEAN-FLO guaranteed to increase bottom oxygen in the deepest water to 3.6 mg/l, and guaranteed to reduce ammonia by 70 percent. CLEAN-FLO designed the project to remove 1.9 mg/l ammonia at highest flow. Method: Two hundred 0.75 hp oilless piston compressors are located in five buildings on the shoreline, forty compressor per building. Weighted air line connects from the compressors to 400 microporous diffusers approximately evenly-spaced on the bottom of the reservoir. Small bubbles rise from the microporous diffusers at the bottom, creating a non-turbulent flow of 227,000 m3/hour (60,000,000 GPM) of water to the surface. When the water reaches the surface, it spreads out 0.04 cm (0.1 in) thick, and flows across the surface. As the water passes through the bacterial culture media, microorganisms lodged on the surface feed on ammonia and phosphorus. Dicer Environmental Engineering Service of Koahsiung, Taiwan, prepared the engineering proposal for the Taiwan government. Dicer performed all construction work at the job site, with the barrier, culture media and inversion/oxygenation system under the supervision of CLEAN-FLO International, Inc. Results: Bottom oxygen fluctuated initially, and then stabilized at 3.6 mg/l. While Dicer was installing the CLEAN-FLO continuous laminar flow inversion/oxygenation, the pig farmers increased the amount of pig manure dumped into the river. This increased ammonia level from the five-year average of 1.8 mg/l to 3.6 mg/l. During the test run, the level of incoming ammonia continued to steadily increase to 7.2 mg/l. The CLEAN-FLO system removed an average of 2.9 mg/l ammonia, far exceeding the design despite the increased level of incoming ammonia. The Water Treatment Company excused CLEAN-FLO from the 70 percent removal requirement. Considering the increased level of incoming ammonia, they conceded that CLEAN-FLO based their design on the five-year average before treatment, and could not anticipate the increased ammonia. Conclusions: The process of continuous laminar flow inversion/oxygenation is a useful tool for blue-green algae infested reservoirs and lakes. It removes bad taste and odor from the finished drinking water. In combination with bacterial culture media, ammonia can be effectively reduced. This process reduces the chemicals needed in the water treatment plant to produce finished drinking water. The inversion and oxygenation do not affect blue-green algae in any way, it simply removes the nutrients that blue-greens feed on, and moves the algae to the bottom of the reservoir where it can not receive sun light. To cover the increased ammonia level, we have added 176 diffusers.
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