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r.r <br /> Technical Description <br /> Criteria: <br /> 50,000 gpd flow t 31%= 0.065 MGD <br /> 0.065 x 250 mg/L x 8.34 x 1000 ft' = 94.11 CFM <br /> 1440 <br /> G. Comminution or screening and, where required, grit removal must precede the aeration/ <br /> equalization chamber. <br /> H. An emergency overflow from the aeration chamber to the buffer tank my be provided. <br /> TERTIARY FILTERS <br /> Tertiary filters are normally designed to accept a suspended solids loading of 20-30 mg/L. Occa- <br /> sional shock loads can be handled; however, the filter will not function properly at continuous <br /> suspended solids loadings of 50 mg/'L or greater. Therefore, design and operation of the secon- <br /> dary plant become an important aspect in the overall efficiency of any tertiary system. <br /> If the secondary treatment plant is operated to produce an effluent with a suspended solids con- <br /> centration of less than 30 mg/L, a properly maintained, designed, and efficiently operated filter <br /> can be expected to remove 95-98.5%, or produce a resultant final effluent suspended solids con- <br /> centration of 1.5 to 5 mg/L. Nitro-Raptor tertiary systems have consistently produced final efflu- <br /> ent with both BOD, and suspended solids in this range. <br /> 7H recommends the use of DynaSand continuous-backwash filters wherever possible. Although <br /> their initial cost is higher than a standard pressure filter, cost of ownership over a period of time <br /> is considerably less, as the DynaSand has no moving parts, it is virtually maintenance-free, and <br /> produces a somewhat more consistent output. DynaSand filters are approved for California Title <br /> 22 Standards for Wastewater Reclamation. <br /> When using a single pressure filter, an important design consideration is the ability of the filter to <br /> accumulate sufficient solids in the media during extended filter runs to eliminate the need for fre- <br /> quent backwashes. Frequent backwashes, Which must be accomplished using a freshwater source, <br /> not only consume energy and plant operator's time but also impose additional hydraulic loading <br /> requirements on the secondary process if the backwash is directed to the aeration chamber. <br /> Because of this additional hydraulic loading, 7H recommends the use of dual filters which are <br /> desiened to use the filtrate of one filter to backwash the other. Since the filtrate is already part of <br /> the system hydraulic loading, nothing is added. In order to obtain the desired solids holding ca- <br /> pability, the media must allow penetration into the depth of the bed rather than simply retaining <br /> solids on the media surface. Conventional filter sands, as used in potable water filtration, provide <br /> only this surface removal and retention effect. This is satisfactory for the low solids concentra- <br /> tions involved in freshwater filtration. However, in wastewater filtration, solids concentrations <br /> are significantly higher and tend to rapidly seal the surface. <br /> During backwash of conventional filter sand media, another phenomenon occurs which contrib- <br /> utes to this surface straining effect. When the bed is fluidized, the less dense; smaller grain-size I <br /> media tends to accumulate as the top layer in the bed. This provides for efficient particle removal <br /> - 16- <br /> 7-H Technical Services Group, Inc. <br />