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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />3.3 Corrected Effective Hydraulic Analyses <br /> <br />In general, the duplicate effective hydraulic models did not consider conveyance within the <br />two irrigation ditches, Arthur Ditch on the north and Sherwood Lateral to the south; this appears <br />to be an accurate representation of the physical operating condition of the system, However, as <br />defined, the left end of three cross sections (Nos, 18625, 19337 and 19830) would allow effective <br />conveyance within Arthur Ditch for either the 100- or 500-year event, while the main portion of <br />the Spring Creek cross section (exclusive of the ditch) could actually contain these flows, <br />Consequently, a corrected effective HEC-2 model was prepared which encroached the left end <br />of these three cross sections in order to preclude flow in the ditch, Inspection of the duplicate <br />effective model also revealed that Cross Section 19337 passes through, or in close proximity to, <br />two spot elevations which were not coded into the model. These two spot elevations (4993,6 and <br />4995,0 ft, NGVD) were also included in the corrected effective model. No other changes were <br />made in the corrected effective HEC-2 models, <br />Several other spot elevations shown on the work maps, located in close proximity to the <br />cross sections downstream of Cross Section 19337, were not included previously in the duplicate <br />effective HEC-2 model. Unlike Cross Section 19337, these spot elevations were not incorporated <br />into the corrected effective model as it appeared they would not materially affect the analysis, <br />This determination was made based on the results of the duplicate effective hydraulic analysis <br />which indicated that the reach within the BNRR detention pond from the upstream face of the <br />railroad embankment to Cross Section 18625 is entirely influenced by backwater during the 100- <br />year event. It is noted that the 100-year water surface profile through this reach is horizontal at <br />the 100-year ponded water surface elevation of 4993,5 ft, NGVD, <br />Results of the corrected effective floodplain analysis were compared to the duplicate <br />effective modeling results, as shown in Table 3,1. Base flood elevations computed by the <br />duplicate and corrected effective models matched at all but two cross sections, At Cross Sections <br />19337 and 19830, the corrected effective base flood elevations differed by -0,1 and +0,1 feet, <br />respectively, compared to the duplicate effective base flood elevations, It is noted that the O,l-foot <br />rise is located at Cross Section 19830 and does not impact any insurable structures, Graphical <br />representation of the corrected effective flood profiles through the current study reach is provided <br />in Appendix B, In addition, graphical representations of the cross sections through the study reach <br />which were modified for the corrected effective analysis are provided in Appendix C. <br />For the corrected effective floodway analysis, floodway encroachments were not modified <br />from those used for the duplicate effective analysis, Results of the corrected effective floodway <br />analysis are summarized in Table 3,3, The table indicates that the floodway water surface <br />elevations are identical to the base flood elevations, thereby meeting the intent of the original <br />floodway analysis through the BNRR ponding area, HEC-2 output for the corrected effective <br />flood plain and floodway analyses is provided in Section C to the Technical Addendum, <br /> <br />T:\OPEN',cocsrtDl "cocsrtDl femJ-LOt\IR tinal-rpL\\pd <br /> <br />12 <br /> <br />ANdERSON CONsulTiNG ENGiNEERS, INC, <br />