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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 /> <br />TABLE III-I <br /> <br />enhanced information design for perviouslimpervious area connections and water quality capture volume were <br /> <br /> <br />not used for the study areas and the program defaulted to the analysis method used for traditional drainage <br /> <br /> <br />practices. Sub-watershed geometries were measured directly from the mapping prepared for this study. The <br /> <br /> <br />impervious percentages used in this study were derived from City and County land use maps and development <br /> <br /> <br />plans and aerial photography. The percent imperviousness for each sub-watershed was estimated as the <br /> <br /> <br />composite value resulting from a weighted area average computation for the various imperviousness zones. <br /> <br /> <br />Several areas within the study limits were examined in detail in order to more accurately determine the <br /> <br /> <br />appropriate composite imperviousness values. <br /> <br />TWO-HOUR DESIGN STORM FOR BASINS BETWEEN FIVE AND TEN SQUARE MILES <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br /> INCREMENTAL RAINFALL DEPTH/RETURN PERIOD <br /> ZONE I <br />TIME 2-YR 5-YR IO-YR 50-YR 100- YR <br />(MIN) (IN) (IN) (IN) (IN) (IN) <br />5 .02 .03 .03 .03 .03 <br />10 .04 .05 .06 .08 .08 <br />15 .09 .12 .14 .11 .12 <br />20 .16 .21 .24 .18 .21 <br />25 .26 .35 .40 .33 .35 <br />30 .14 .18 .19 .55 .62 <br />35 .07 .08 .09 .26 .35 <br />40 .05 .06 .07 .18 .21 <br />45 .03 .05 .06 .11 .16 <br />50 .03 .05 .05 .11 .13 <br />55 .03 .04 .05 .07 .10 <br />60 .03 .04 .05 .07 .10 <br />65 .03 .04 .05 .07 .10 <br />70 .02 .04 .05 .05 .05 <br />75 .02 .04 .05 .05 .05 <br />80 .02 .03 .04 .04 .03 <br />85 .02 .03 .03 .04 .03 <br />90 .02 .03 .03 .03 .03 <br />95 .02 .03 .03 .03 .03 <br />100 .02 .02 .03 .03 .03 <br />105 .02 .02 .03 .03 .03 <br />110 .02 .02 .03 .03 .03 <br />115 .01 .02 .03 .03 .03 <br />120 .01 .02 .02 .03 .03 <br />TOTAL 1.18 1.60 1.85 2.54 2.93 <br /> <br />Detention, retention and infiltration parameters were assigned to each hydrologic soil group as <br /> <br /> <br />recommended in Tables 2-1 and 2-2 of tbe Runoff Chapter of the USDCM. Parameters were then determined <br /> <br /> <br />for each sub-watershed using the predominate soil zones. A summary of the COOP parameters used for the <br /> <br /> <br />analysis are presented in Table lII-2. <br /> <br />D. STORM WATER MANAGEMENT MODEL <br /> <br />The personal computer version of the UD&FCD SWMM was used to route the COOP-generated <br />runoff hydrographs. The version of the model used was UDSWMM3. The routing element parameters <br />required for SWMM are: element number, type (e.g. channel, pipe, etc.), length, slope, and Manning's "n" <br />value. The type of SWMM routing elements used were based on the existing drainageway configurations and <br />shapes. <br /> <br />For streets and storm sewers, a Manning's "n" value of 0.020 was used. For existing channels, the <br /> <br /> <br />Manning's "n" value was estimated using Equation 2 recommended in the SWMM users manual (Reference <br /> <br /> <br />2). The SWMM routing element parameters used for this study are presented in Table III-3. <br /> <br />Existing systems for the baseline flow rouling modeling included all structures that are currently in <br />place. Structures that are expected to be constructed in the near or distant future as part of the Big Dry Creek <br />Master Plan are not included in the baseline run. These future facilities (i.e. alternative detention ponds) have <br />been modelled as part of the alternatives evaluation Dhase of this project. None of these future facilities are <br />used for this FHAD study. The SWMM routing elements are shown on Figures III-2A, B and C. <br /> <br />Only detention ponds which are publicly owned and maintained were included in the SWMM routing. <br />Storage-discharge relationships were taken from drainage studies approved by Douglas County (References <br />4, 5, 6, 7, 8, 9) and are tabulated in Appendix A. <br /> <br />111-5 <br />