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in n <br /> 11-2 REMOVAL MECHANISMS IN PACKED-BED FILTERS 709. <br /> i <br /> (a) t dose/d (b) 4 doses/d (c) 24 doses/d <br /> Applied liquid dose fills the Applied liquid dose partially Applied liquid dose flows <br /> interstices of filter medium fills the interstices of the around filter medium in a <br /> I allowing some influent particles filter medium. thin film. Most interstices <br /> to pass through the filter are open. <br /> F untreated. <br /> FIGURE 11-6 <br /> Effect of hydraulic application rate on flow through filter: (a) 1 dose/d, (b) 4 doses/d,' <br /> and (c) 24 doses/d. <br /> i <br /> microorganisms can pass through the filter untreated (Fig. 11-6a). As the volume <br /> applied per dose is reduced, partially unsaturated flow occurs (Fig. 11-6b). If the <br /> volume applied per dose is reduced further, the liquid will flow around the filter <br /> medium in a thin film (Fig. 11-6c). When film flow occurs, the soluble and colloidal . <br /> I material in the wastewater is absorbed, and oxygen from the air in the open intersti- <br /> tial space is transferred across the thin liquid film to the aerobic bacteria responsible <br /> for oxidation of the organic carbonaceous materials. It should be noted that the con- <br /> centration <br /> - ; <br /> I centration of oxygen in air is about.250 mg/1- at 20°C. Because absorption and the <br /> high oxygen concentration in air play such an important part in the operation of both <br /> IPBFs and RPBFs,it is imperative that the applied liquid flow over the filter medium; <br /> in a thin film,-if the sin pass filter is to function most effectively. <br /> E Wh6d.ihe�flow,is in a.,thin film,_the-oxidation of carbonaceous materials will <br /> occur.tn.the upper portions,of,the filter.bed: Simultaneously, ammonia will be con- <br /> verted to nitrate.(nitrificatio_n). In turn, the nitrate will be converted to nitrogen gas <br /> (denitrification) in anoxic.microsites within the filter. Biological denitrification has f, <br /> been shown to occur under anoxic conditions and,for certain bacteria,under aerobic <br /> conditions (Robertson and Kuenen, 1990). The organisms responsible for denitrifi- <br /> cation utilize adsorbed.carbon in particulate matter as the energy source. To sustain <br /> the performance of the filter, the microorganisms in the filter must be maintained ' <br /> in the endogenous growth rate. if too much organic material is applied, the bacte— <br /> rial growth rate will increase and the accumulation of material can occur, ultimately <br /> leading to failure, as described later. <br /> Flow in a thin film is especially important if viruses are to be removed.In a recent <br /> study,it has been demonstrated that the formation of a uniform dense bacterial film, <br /> produced by increasing the number of doses per day, will have a significant effect on <br /> virus removal(Emerick et al.;A997a).Although sintered glass was used as the filter- <br /> ing medium,a similar effect was observed with sand,as shown in Fig. 1 l-7(Emerick <br /> i <br />