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Scope : <br /> The PC South Algal Turf Scrubber(D Pilot was implemented with the intent of <br /> determining the applicability of the technology to meet targeted performance <br /> goals and identifying critical performance parameters to be applied to a proposed <br /> full scale Algal Turf Scrubber® system to be designed to provide 1 ) reduction <br /> and recovery of nutrients from the South Canal within Indian River County , as <br /> managed by the Indian River Farms Water Control District ( IRFWCD) and 2 ) <br /> elimination of biological toxicity associated with a Reverse Osmosis ( RO ) <br /> Concentrate . The operational protocol originally delineated for the pilot was to <br /> dilute the RO Concentrate with the water from the South Canal at a proportion of <br /> about 10 % RO concentrate . <br /> The pilot investigation was initiated on 1 / 17/2011 . Laboratory data to date <br /> provides indication that the system at the stated dilution does render the blended <br /> water non -toxic , and is effective in removing and recovering both nitrogen and <br /> phosphorus at rates within expected ranges . To this extent , the system appears <br /> applicable and appropriate for meeting the project intent at a 10 % RO <br /> Concentrate , 90 % Canal water blend <br /> Based upon reviews by the County staff and HydroMentia of historical flow <br /> patterns within the South Canal in the vicinity of the proposed full scale facility , it <br /> was determined that flows within the canal would not always be sufficient to <br /> ensure the 90 % dilution of the RO Concentrate , which is projected to have a <br /> constant flow rate of about 1 MGD . Consequently , it was decided that based <br /> upon the worst case low flow conditions within the canal of 1 MGD , that the most <br /> conservative dilution would be 1 : 1 , or 50 % RO Concentrate and 50 % Canal <br /> water . To accommodate this design feature , it was decided that the pilot system <br /> should be adjusted to receive a 1 : 1 blend , and assessed accordingly both in <br /> terms of nutrient removal and toxicity . <br /> Because the shift in the influent blend will result in a significant increase in <br /> conductivity (salinity) , it will be necessary to change the bioassay protocol from <br /> freshwater species (fathead minnows and daphnia ) to marine/estuarine species <br /> ( mysid shrimp and menidia minnows ) . To adequately assess the toxicity of this <br /> new blend , six additional bioassay tests will be required , using these <br /> marine/estuarine species . Three of these will be acute tests , which if found non <br /> toxic , will be followed by three chronic tests . <br /> Following about 12 weeks of operation under the new blend conditions , the <br /> system will be again returned to the 10 % RO Concentrate blend , and planned <br /> chronic bioassay testing of the freshwater species will be completed . This revised <br /> program will not only allow assessment of the efficacy of the technology under <br /> these two conditions , but will permit assessment of performance during the <br /> transitional period associated with changes in blends , during which time the algal <br /> turf community will undergo ecological adjustments . <br />