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 Page 12 Upper and Lower Emerald Valley Dam Failure Report <br /> January 23, 2015 <br /> <br /> <br /> <br /> <br /> Figure 14: Comparison of Sept 2013 Storm to NOAA Atlas 14 Precip Frequency Estimates <br />The above intensity data shows clearly that the Sept. 2013 storm was not <br />extremely intense. The maximum hourly intensity in the storm has less <br />than a 1-year Average Recurrence Interval (ARI) by NOAA Atlas 14. <br /> <br />However, the Sept 2013 storm event was a long slow rain: the 48-hour <br />total for Sept 12 and 13 for Little Fountain Creek Above Highway 115 are <br />just below a 500-YR ARI. Figure 14 plots observed rain totals for Little <br />Fountain Creek at various durations (maximum total for each duration) <br />along with NOAA Atlas 14 (NA 14) frequency estimates (full NOAA Atlas 14 <br />tabular data are include in Appendix D). Figure 14 shows the Sept 2013 <br />maximum 15 minute, 1 hour, and 6 hr rains were well below the NA 14 <br />100-YR estimate. For the 24-hour duration the Sept 2013 rain was <br />approximately equal to the NA14 100-YR estimate. The maximum observed <br />48-hr total was between the NA 14 100-YR and 500-YR estimates. <br /> <br />7.2 Model Setup & Calibration <br />The results of the field investigations, basin delineation, and rainfall data analysis all <br />provide important parameters to be able to model the physical system of the basin as <br />rain falls and water runs off into the stream networks. Those previously discussed <br />parameters are all fixed once determined. However, unit hydrographs, basin loss <br />parameters, channel routing parameters, and dam breach parameters are all more <br />subjective. This results in an iterative process being utilized to select the most <br />appropriate values of each of these parameters. This process is referred to as the <br />“calibration phase” of the modeling. <br /> <br />The hydrologic literature typically assigns ranges of appropriate values for these <br />parameters. In the modeling process an initially assumed set of parameters is utilized; <br />the model is run and then the modeled outflow values are compared to those <br />calculated through indirect methods at locations of interest. The parameters <br />determined to be sensitive, meaning their small change results in significant changes <br />in model results, are modified, staying within the appropriate ranges, until the model <br />results compare favorably with the measured flows at those sections of interest, the <br />calibration sections.