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Akron Water Pollution Control Station No Feasible Alternative

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listed in Section 4.2.1. The 120 MGD alternative will be referred to as <strong>Alternative</strong> 1. Refer to<br />

Figure 4-1.<br />

A variety of other process alternatives were considered for increasing the secondary treatment<br />

capacity. These alternatives, upon initial screening, were organized into five groups. For any<br />

alternative which provides additional secondary treatment capacity, it is assumed existing<br />

facilities are upgraded to increase the 110 MGD capacity to 120 MGD.<br />

Group 1 <strong>Alternative</strong>s – Single Stage Nitrification Processes<br />

This group includes single stage nitrification processes, including oxidation ditches, vertical loop<br />

reactors, step-feed aeration, and high rate pure oxygen that may be employed either within<br />

existing tankage and/or in additional, new tankage. With this group of alternatives the primary<br />

settling tanks would be removed from service in order to increase the organic and nutrient<br />

loading to secondary treatment sufficiently to support additional mixed liquor capacity. Along<br />

with this increased capacity would come additional final settling tanks.<br />

These Group 1 alternatives are screened from further evaluation for the following reasons:<br />

• Having additional mixed liquor in suspension will increase annual operation and<br />

maintenance (O & M) costs for blower operation and yield no treatment improvement. The<br />

sludge settleability may actually deteriorate due to increased sludge retention times (SRTs)<br />

• Abandonment of the primary settling tanks will impact the existing sludge process train that<br />

includes a compost facility for final stabilization and disposal, and a planned anaerobic<br />

digestion process being initiated in 2007. A significant investment would be required to<br />

reconstruct the sludge process train to treat solely waste activated sludge. The sludge<br />

processing costs would be higher then the current cost for composting. And, final disposal<br />

costs will be significantly higher for land application as compared with the current compost,<br />

most of which is sold in bulk or bag to consumers.<br />

Group 2 <strong>Alternative</strong>s – Conventional and Attached Growth Processes<br />

Conventional activated sludge, contact stabilization, rotating biological contactors (RBCs),<br />

Submerged Biological Contactors (SBCs), and trickling filters are included in this group. All<br />

Group 2 alternatives require the primary settling tanks remain in service to reduce the organic<br />

and nutrient loading; and, they have shorter hydraulic detention times and shorter SRTs. The<br />

sludge produced is typically more settleable as supported by the Recommended Standards For<br />

Wastewater Works 2 (Ten States Standards) which allows higher surface overflow rates (SOR)<br />

and peak solids loading rates for settling tanks following these processes. The existing final<br />

settling tanks, in theory, could process higher peak flows up to approximately 170 MGD based<br />

on these SORs.<br />

The major problem for the Group 2 alternatives is that sufficient nitrification will not occur with<br />

these processes to achieve ammonia nitrogen levels meeting the City’s NPDES Permit. There<br />

are also other unacceptable aspects of these alternatives. First, effluent CBOD5 concentrations<br />

would also likely be higher than currently achieved with the existing single stage nitrification<br />

process. Second, several hydraulic restrictions within piping and conduits would still need to be<br />

addressed to process any increased flows through the secondary system. Third, the peak solids<br />

loading rate on the FSTs would become a limiting factor and restrict peak flow to a marginal<br />

increase above the current capacity.<br />

Page 4-6

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