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<br />~ <br />r <br />i <br />I <br />I <br />I <br />I <br />I <br />I <br />i <br /> <br />the reduction in TSS produced by the <br />filter itself. <br />Eo. = 101 mgll <br />~: Using Equation 7 estimate the <br />average annual TSS load removal by the <br />filter. <br />1..., = 263 Ibs <br />SIm1!: Determine the filter's annnal <br />maintenance frequency. Assume m = 1 <br />(i.e., once per year). <br />Steo 7: To keep the size of the filter <br />small while not imposing a very <br />frequent maimenance schedule we <br />choose to design the filter to drain at <br />approximately 2.0 inches per hour. This <br />means L.. = 0.32 pound/square foot in <br />Figure 3. <br />~: Using Td = 12 hours and C = <br />0.66 from Step 2 and a from Figure 1 in <br />Equation 1, find the maximized WQCV: <br />p. = 0.32 watershed inches = (1720 ft'l <br />~: U~ Equations 9 and 10: <br />Arm = 822ft' <br />Aa. = 871 Jf <br />S!mlQ: The two areas are within 20% <br />of each other. Choose the larger of the <br />two. <br />Aj = 870 sq. ft (after rounding off) <br /> <br />Examole 2. Same as Example 1 except <br />use a filter inlet, namely Case 3, with /)! <br />=0.5. <br />SleDs 1 throul!h 3 are the same as in <br />Example 1. <br />~. Using Equation 5 for a <br />"retention basin" with a 12-hom drain <br />time find: <br />Eo. = 124 mgll <br />~. Using Equation 7 we find <br />1..., = 3221bs <br />SIm1!. Assume m = 1. <br />~. Using the same reasons stated in <br />Example 1 we find: L",=O.32lbs1 sq. jI. <br />~: Same as in Example 1 @ Td = <br />12 hrs.: P.=O.32 inches (1,720cu.jI.) <br />~: Using Equations 9 and 10: <br />Arm = l006fr <br />Aa. = 871 Jf <br />~: The two are within 20".4 of <br />each other. Use the larger of the two. <br />Arl,oooJf. (after rounding off) <br /> <br />Espected Water Quality Performance <br />Figure 4 illustl3tes two cases during <br />larger storms, namely overtlow of the <br />excess and the bypass of the excess. To <br />make a valid asse9~mP.11t of the average <br />annual FMC for any constituent <br />reaching receiving waters, to flow- <br /> <br />weight the concentrations of the effluent <br />and the excess runoff from all the <br />storms that occur, on the average, any <br />given year. For Case I shown in Figure <br />4 this is given by Equation 11 <br /> <br />Ec =(k,.'kD.E,)'(I-r.)+Ej 'r. (11) <br />and for Case 2 by Equation 12 <br /> <br />Ec =(k,.'E;)'(I-rlf)+Ej.rlf (12) <br /> <br />In whi::h, <br />Ec ~ average annual EMC downstream <br />of the filter facility, in mgll <br />E, = average annual EMC in the runoff <br />inflow to the WQCv, in mgll <br />Ej = average annual concentration in the <br />filter's effluent, in mgIl <br />r" = fraction of the average annual <br />runoff volume that flows through the <br />filter <br />kD = fraction of the original EMC in the <br />runoff that remains in the water after <br />overflows <br />kT = coefficient of the EMC that <br />represent the post "first-flush" fraction <br />of the average EMC in stormwater <br />runoff <br />if the maximized coefficients in <br />Figure 1 are used, one can expect <br />r, = 0.8 to 0.9. If, however, the runoff <br />from the mean storm is used, one can <br />expect r,,= 0.65 to 0.7. <br />Currently it is not possible to <br />suggest defiuitive values for kn and kn <br />which coefficients depend on the <br />constitoent being considered and the <br />actual design. However, a Iiteralore <br />review by the author suggests the <br />following tentative ranges for TSS: <br /> <br />k,,=O.3 to 0.5 k,=0.7 to 0.9 <br />Table 2 summarizes, after screening <br />out the outliers, the findings of filter <br />tests at four cities in the United States, <br />namely, Alexandria, VA; Austin, TX; <br />Anchorage, AK; and Lakewood, CO. <br />Data for the first three were <br />consolidated by Bell et al. (1996) and <br />the data for the Lakewood site were <br />obtained by the Urban Drainage and <br />Flood Control District in 1995. Note <br />the high variability in the influent <br />concentrations for all constituents and <br />that the ratios between the high and the <br />low concentrations are siguificant1y less <br />for the effluent. The variability in the <br />influent quality accounts for most of the <br />range in the reported removal <br />percentages. <br /> <br />13 <br /> <br />In Example 1 an extended detention <br />basin was used upstream of the filter. It <br />is relatively easy to design this <br />arrangement so that all runoff will pass <br />through the detention basin and the <br />excess runoff will overtop the pond. <br />Let's further assume that kn = 0.35 and <br />kr= 0.75 and as a first order estimate <br />assume that 80% of the average annual <br />runoff volume will pass through the <br />basin and the filter. Using an average <br />effluent TSS concentration of 16 mgIl <br />(fable 2), the average annual EMC of <br />TSS downstream of the fiher installation <br />is <br />Eo = 25 mgll <br />Comparing this to the average EMC for <br />TSS in stormwater runoff at that site <br />(i.e., 225 mgIl), this installation will <br />have 82% average annual removal <br />efficiency for TSS. <br /> <br />Acknowledgments <br />The author wishes to acknowledge <br />the support of the Urban Drainage and <br />Flood Control District and City of <br />Lakewood in the building and testing of <br />this test filter indal1Ation. Many thanks <br />to L. Scott Tucker, the District's <br />Executive Director, for his continuing <br />support of scientific exploration. <br />The author is also grateful to John <br />Doerfer, Richard Ommert, Curtis <br />Neofeld, Jerry Goldman, Chris <br />Jacobson, Warren Bell, Richard Horner, <br />Betty Rushton, Eugene D. Driscoll, <br />Jonathan E. Jones, Jiri Marsalek, Bill <br />Pisano, William P. Ruzzo, George <br />Chang and James C.Y. Guo for their <br />help, support and/or review and <br />comments on the original paper and to <br />GaIene Bushor for sotting through and <br />making sense of the author's hand- <br />written manuscripts. <br /> <br />Refereaces <br />BoIJ, w. StoIceo, 1.-, 0...... 1.-1. ondNguyen, T. <br />1966 (undaI<>d). b...._ of tho PoIhaQllt <br />RBmowIl FJflc/enclu ofDekrwa... Sartd Flit.,. <br />BMP<. City of A1elWldria, DoportmoDI of <br />Tnooportatioo. ond Enviroo.meolal s..m-, <br />A1exmdria,VA <br />DriIooU, E.D., PIIhegyi, O.E., SII'el:ker, E. W. aDd <br />SbeIIoy, P,E. 1989. Ana/y.I. ofSkJrm Evonu <br />Charactorl8llt:.for s.Iected Ratn{aU Gallgu <br />7'hrotIg",,"IIM Un/1M Statu. U.s. <br />Enviroo.meolalProtodioo. Agency, <br />WubiJIstoo., D.C. <br />EPA 1983. Rau/tJtoflheNati01lWtdo Urban <br />llJUIoffProgram, FlnaIJleport. U.S. <br />_Protodioo.Agfmcy,NTIS <br />PB84-18"2, W_alU"gfl1ll D.C. <br />