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11-4 MULTIPASS (RECIRCULATING)'PACKED-BED FILTERS 743 <br /> TABLE 11-13 <br /> Nitrogen removal by recirculating filters <br /> Medium Loading..:..- - -•----- <br /> size, rate, Total nitrogen,mg/L Percent <br /> Location mm gal/W-d' Influent Effluent removal <br /> Oregon(Ronayne, 1984) 1.2 1.5 58 32 45 <br /> Paradise,California(Nolte and Associates, 1992)• 3.0 4.3 63 35 44 <br /> Paradise, California(Nolte and Associates, 1992) 3.0 2.5 57 26 54 <br /> Florida(Sandy et al., 1988) 2.4 3.8 55 9.6 82 <br /> '(9aVft2-d)x•40 = mmld <br /> 1 - <br /> Table 11-13. Nitrification and denitrification are responsible for the removal. In- <br /> crease- 'riitr`ogen removal can be achieved by using"flooded underdrains to-enhahcef <br /> denitrification, following the filter with an anaerobic filter, or addin • a supple- <br /> -mental carbon source, If the ammonia level is high (over 60 mg/L), and alkalinity <br /> levels are low, nitrification can reduce the pH excessively. As ammonia is nitrified; <br /> 7.14 mg of alkalinity, expressed as calcium carbonate (CaCO3), is destroyed for <br /> every 1 mg of ammonia oxidized to nitrate (see Example 2-9 in Chap. 2). If the <br /> community water supply is a soft,- ow-alkalinity water, there may be insufficient <br /> alkalinity to buffer the pH during nitrification.If the pH is reduced through the filter, <br /> the overall performance of the bacteria for removal of BOD and ammonia can be <br /> impaired. A source of alkalinity,such as sodium or calcium carbonate,can be added. <br /> Alternatively, the denitrification process, which restores about half of the alkalinity <br /> lost in nitrification, can be maximized. Alternatives to maximize nitrogen removal . <br /> with recirculating sand filters are discussed in Sec. 11-6. <br /> Design Considerations , <br /> Important factors in the design of RPBFs include type and size of filter medium, <br /> depth of filter bed, hydraulic loading rate, organic loading rate, dosing frequency <br /> and rate, distributed dosing, and modular design. These design considerations are <br /> l examined in the following material. Typical design criteria for recirculating filters <br /> are presented in Table 11-14.The design of an RPBF is illustrated in Example 11-6. <br /> Type.,and size of.-filter media. The types of filter media used for RPBFs <br /> range from coarse sand to bottom ash to fine gravel.The finest medium reported was <br /> a sand with an effective size of 0.3 mm(Belicek, 1986).Excessive clogging and short <br /> filter runs were observed with this sand size, and the investigators recommended an <br /> increased sand size of 0.6 mm. Screened bottom ash has been used in sizes ranging <br /> from 0.9 to 2.4 mm. The range of the medium sizes for gravel filters is from 1 to <br /> 6 mm. A typical value for a fine gravel size is 2.5 mm.When fine gravel larger than <br /> 3 mm is used, a sharp drop in the degree of nitrification has been observed(Ball and <br /> Denn, 1997). <br /> i <br />