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Akron Water Pollution Control Station No Feasible Alternative

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<strong>Alternative</strong> 3A will include four (4) new, 42.5 MGD high-rate treatment processes to<br />

provide clarification/filtration of final settling tank overflow plus the necessary hydraulic<br />

improvements up to 170 MGD. Refer to Figure 4-4.<br />

<strong>Alternative</strong> 3B will include five (5) new, 42.0 MGD high-rate treatment processes to<br />

provide clarification/filtration of final settling tank overflow plus the necessary hydraulic<br />

improvements up to 210 MGD. Refer to Figure 4-5.<br />

<strong>Alternative</strong> 4 – Membrane Filtration<br />

This alternative considers the application of wastewater membrane technology to filter the<br />

mixed liquor effluent from the aeration basins to provide the necessary additional clarification<br />

capacity. The membrane filters would work in concert with the existing final settling tanks.<br />

Based on a review of this concept with two leading manufacturers, it is proposed to locate the<br />

membranes in separate, new tanks north of Aeration Basin <strong>No</strong>. 6. The required pumping and<br />

piping systems would be similar to <strong>Alternative</strong> 2. Use of membranes will require fine screening<br />

of primary effluent and primary effluent pumping. A two or three millimeter screen size is<br />

recommended. Because of the additional hydraulic head required for this alternative, it will be<br />

necessary to significantly modify the secondary influent flow splitting chamber (Aeration Influent<br />

Flume). The aeration basin walls will be raised. Two capacity increase increments were<br />

evaluated.<br />

<strong>Alternative</strong> 4A will include two membrane filtration tanks to provide 40 MGD additional<br />

solids separation capacity plus the necessary hydraulic improvements and a new Fine<br />

Screening and Pumping Facility, for a total secondary treatment capacity of 160 MGD. Refer to<br />

Figure 4-6.<br />

<strong>Alternative</strong> 4B will include four membrane filtration tanks to provide 80 MGD additional<br />

solids separation capacity plus the necessary hydraulic improvements and a new Fine<br />

Screening and Pumping Facility, for a total secondary treatment capacity of 200 MGD. Refer to<br />

Figure 4-7<br />

Group 5 <strong>Alternative</strong>s – Membrane Bioreactor (MBR) Facility<br />

The aeration basins would be converted to membrane bioreactor tanks in this alternative.<br />

Because MBRs function with a much higher mixed liquor suspended solids concentration<br />

(approximately 10,000 mg/l), not all of the six aeration basins will be needed. A new fine<br />

screening (two to three millimeter) facility would be located upstream of the MBR tanks following<br />

primary treatment (primary settling tanks will remain in service in order to maintain the current<br />

sludge process train). To accommodate the headloss imposed by the fine screens, and provide<br />

a deeper tank depth as required for the MBR equipment, it is proposed to pump primary effluent<br />

to the new fine screening and MBR facility. Because the Cuyahoga River 25-year flood<br />

elevation impacts WPCS effluent hydraulics, a primary effluent pumping station will also be<br />

required. Permeate pumps will draw mixed liquor through the membranes and discharge the<br />

filtrate to the secondary effluent conduits. Piping galleries will be required between<br />

compartmentalized sections of the modified aeration basins to provide space and access to<br />

influent and effluent piping and to access the permeate pumps. Two capacity increase<br />

increments were evaluated.<br />

<strong>Alternative</strong> 5A will include the conversion of three (3) aeration basins into MBR tanks<br />

with an average day capacity of 90 MGD and a maximum day capacity of 170 MGD. A primary<br />

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