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754 CHAPTER 11: Intermittent and Recirculating Packed-Bed Filters <br /> TABLE 11-17 <br /> Typical design criteria for layered textile filter with capillary <br /> break between every 4 in of textile medium used to treat typical <br /> residential wastewater' <br /> Hydraulic <br /> loading rate,gailftZ d f=ilter Dose <br /> Type of depth, limit,' <br /> operation Designtt Peak' in galfft2 <br /> Single pass 15 30 24 0.5 <br /> Recirculation 30 45 12 0.5 <br /> 'Bounds(1996). <br /> +Based on typical average daily flows(e.g.,50 gal/capita-d). <br /> I Average residential septic tank effluent from a septic tank with an effluent filter:BOD = <br /> 130 mg/L,TSS = 40 mg/L,and O and G = 20 mg/L. <br /> 'Peak residential septic tank effluent from a septic tank with an effluent filter:BOD= <br /> 200 mg/1.,TSS = 60 mg/L,and O and G = 25 mg/L. <br /> THydraulic application rate,in both cases,should be limited to 0.8 in/dose(20 mm/dose). <br /> at a hydraulic loading rate of 45 gal/ft2-d (1800 L/M2-d) and a 5 to 1 recirculation <br /> ratio, three 4-in (100-mm) layers have proven to be very effective (see Table 11-16) <br /> (Auger, 1997; Chenier, 1997; and Roy, 1997). <br /> To reduce space requirements and construction costs,the final design of the lay- <br /> ered filter is still being optimized with respect to layer thickness, number of layers, <br /> nature of the textile fibers, and compression rate. Current (1997) recommended de- <br /> sign criteria for layered intermittent and recirculating textile filters used for treat- <br /> ing typical residential septic tank effluent are presented in Table 11-17. The textile <br /> medium must be placed in compacted layers not less than 4 in (100 mm) deep. <br /> Peat Filters <br /> The use of peat filters as an alternative method of biological and physical treat- <br /> ment of septic tank effluent has been reported since 1984 (Brooks et al., 1984). <br /> These filters were used in Maine and Ontario (see Fig. 11-30). The peat is a per- <br /> meable, absorbent medium that serves: (1)to filter the wastewater, (2) as a substrate <br /> for biological treatment, and (3) to reduce phosphorus concentration. Loading rates <br /> are usually the same as for intermittent sand filters, 1 gal/ft2•d (4 cm/d). The re- <br /> sults of monitoring several onsite peat filters are reported in Table 11-18. Commer- <br /> cial peat filters are available for individual home use. One manufacturer markets a <br /> 150 ft2 (13.9 m2) filter for the treatment of 500 gal/d (1892 L/d) of septic tank ef- <br /> fluent. The manufacturer emphasizes the ability of the filter to reduce BOD, TSS, <br /> ammonia, and bacteria. <br /> The importance of the source and characteristics of the peat have been demon- <br /> strated,based on the monitoring results obtained in Maine and in Ontario. The spec- <br /> ifications of the State of Maine require a von Post decomposition of H-4, a pH of <br /> 3.5 to 4.5, and a moisture content of 50 to 60 percent. It was observed that peat <br /> from different sources provided various levels of treatment,leading to the additional! <br /> requirement for a nitrate analysis of the peat leachate extract. <br />