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11-2 REMOVAL MECHANISMS IN PACKED-BED FILTERS 711 <br /> waste products, and other debris retained in the filter from the previous dose. The <br /> material flushed from the filter tends to accumulate in the bottom of the recirculation <br /> tank. In highly loaded multipass filters, a solids trap should be included to remove <br /> the material flushed from the filter before the effluent is discharged. <br /> Failure of Single- and Multipass Filters <br /> I Both single- and m- ultipas"s filters can fail when the.hydraulic; solids, and/or organic <br /> 'application rates exceed certain limits specific'to"each type`bf filter. The typical <br /> failure mode is manifested by surface ponding.between liquid applications. In some <br /> cases, the applied liquid overflows the enclosure. Failure usually occurs as the result... <br /> of the accumulation of untreated organic and inorganic solid materials and oil and <br /> grease from the influent, and residual cell tissue that has not undergone endogenous <br /> respiration to such an extent that the pore space becomes clogged. Other causes of <br /> failure include clogged underdrains and the presence of too many fines in the filter <br /> medium. <br /> When the amount of dissolved and particulate organic material applied exceeds <br /> the amount of food needed to maintain the microorganisms in the slime.layer in'a <br /> low growth rate, an increased growth rate will occur. For the purpose of illustration, <br /> assume only soluble organic constituents are applied to the filter. Further, assume <br /> the microorganisms on the surface of the filter medium are capable of absorbing an <br /> excess amount of organic matter. During the time until the next dose, the organisms <br /> will process the stored organic matter,-converting some of it to cell tissue. If there <br /> is not sufficient time for the organisms to reduce their mass through endogenous <br /> respiration between liquid applications (doses), the mass of organisms and unpro- <br /> cessed organic matter in the slime layer will gradually increase with time. As the <br /> film thickness increases, the rate of oxygen transfer and, in turn, biological activity <br /> is decreased, ultimately leading to the failure of the filter. <br />` in a similar manner, if particulate organic matter and oil and grease are applied <br /> and trapped in the slime layer, the organisms in the slime layer must be able to <br /> solubilize and process the applied constituents before the next dose.If they are unable <br /> to do so, a gradual accumulation of solids will occur within the filter, ultimately <br /> leading to failure as evidenced by ponding: A solids balance for a filter is presented <br /> in Example 11-1 to illustrate that,if the filter is loaded lightly,it will take a very long <br /> h <br /> time to clog. <br /> EXAMPLE 11-1. SOLIDS BALANCE FOR AN INTERMUTENT SAND FILTER. Prepare a solids <br /> balance for an intermittent sand filter to assess how-long it would take to fill half of the <br /> void space in the upper 6 in (150 mm)of the filter bed, assuming that 60 percent of the <br /> material retained in the filter is accumulated in the upper portion of the filter. Assume <br /> the following conditions also apply.The values for the influent BOD and TSS are based <br /> on the use of an effluent filter as described in Chap. 5.- <br /> 1. <br /> :1. Filter depth = 0.6 m(2 ft) <br /> 2. Porosity for sand = 40% <br /> 3. Average hydraulic loading rate = 40L/m2•d (1.0 gal/ft'-•d) <br /> 4. influent BOD = 130 mg/L <br /> I <br /> i <br /> f <br />