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<br />!t <br />fr <br />f. <br />~ <br />~ <br />.~t- <br />ti. <br />F <br /> <br />Tile one exception is that the ponding area at station 290+00 IIould be required <br />to store the entire inflO1J volur:le (57.9 acre-feet) of the 5-year rainfall <br />because the outlet IIoulJ be blocked by the coincident 25-year flood (46,500 <br />c.f.s.) on the Arkansas River. A storage area 600 feet ,.;ide by 1,300 feet <br />long IIith a maximum usable depth of 3.8 feet would be excavated to-provide <br />this storage. The outlet size was adjusted so that ponding from the 25-year <br />storm lJOuld not exceed the storage capacity. <br /> <br />~ <br />'- <br /> <br />7-16. Infil tration values selected to determine the outflm-l hydrographs <br />for the subareas varied fror:l 0.70 inch per hour for cultivated land to 0.50 <br />incil per hour for urban areas. The I-hour J 25-year recurrence interval rain- <br />fall (2.30 inches) was used to determine the volume of outflolI from each <br />subarea. Studies of substantial rainfall coincident \vith flood stages in t'ne <br />Arkansas River indicate about 45 percent chance .of occurrence. Triangular- <br />sllaped storm hydro graphs Here cons tructed for the subareas. The storm <br />llydrographs were routed using the Successive-Average-Lag-Hethod (Tatum) to key <br />points. Routed flmls were combined ,-lith side drainage flmJs at appropriate <br />points to obtain design discharges for the collection system conveying interior <br />drainage runoff to the levee outlets. In the routing of flm,s to levee out- <br />lets, consideration was given to the effects of existing structures on peak <br />fImvs. <br /> <br />7-17. Area AI' plate 29, would be separated from area A2 by a section of <br />relocated, elevated irrigation ditch. The point of concentration for area Al <br />,""auld be at station 84+75. The point of concetration for area AZ \'lould be at <br />the outlet at station 107+50. Runoff from area AI' was routed to and combined <br />with runoff from area A2 at station 107+50. The point of concentration for <br />area n would be at the outlet at station 290+00. The runoff hydrographs from <br />the remaining subareas on the right bank "ere routed to key points along the <br />interior drainage ditch to design the ditch and ditch structures to the outlet <br />at station 473+00. The runoff hydrographs for the subareas on the north bank <br />"\vere routed through existing drainage structures on State lligln.,ray 194 and <br />furt11er routed to the levee outlet structure at station 352+DOi\I to design t~le <br />interior drainage collection ditch from station 324+00N to station 351+00" <br />and also from station 355+70N back to station 352+00N. Interior drainase data <br />is tabulated in table 2. <br /> <br />7-18. Areas of easements, ponding excavations, ana outlet structure <br />sizes \Jere varied to obtain the most feasible and economic combinations. <br />Generally an increased cost of installing larger ontlet structures rpc;ultcu. in <br />a savin[;s by reduced easements since stages in the retention pools di<l not allow <br />spread beyond the designated areas (stage A). 'f~1is is cnaracteristic of Cue <br />flat t~rrain. Hhen flmvs exceed the capacity of ti.le ponding area and inundate <br />the flat surrounding area, easement costs increase sharply. The design pool <br />elevations Here lm.Jered to raaintaj.n spread '.Jithin the limits of the cIesir;nnted <br />areas 'uy routing the runoff resulting from the I-hour, 25-year recurrellC2 <br />interval storn throuGh lareer outlets. Iiydrologic data for outlet structur2S <br />and pondinc areas is shm;n on ?late 30. A comparison of the rcquirel! ponc.ia~ <br />for ,'jt2Ges A (r,linor adverse effect~) and C (major adverse effects) is given <br />belm-] . <br /> <br />',- <br /> <br />12 <br />