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Knight Piesold <br /> CONSULTING <br /> Environmental Department, Meg Burt, Senior Manager October 8, 2018 <br /> Cripple Creek and Victor Gold Mining Co. (Newmont) <br /> due to the expansion of the Squaw Gulch Valley Leach Facility (VLF) 2. CC&V directed Knight Piesold <br /> to reevaluate this EMP based on the reduced area. Once VLF 2 construction activities commence, the <br /> existing storage and spillway conveyance capacities of EMP 8c will be sufficient to meet the design <br /> criteria. Furthermore, voids (fissures below the ground surface created from historic mining operations <br /> and local geology) in the area of EMP 8c could pose a safety hazard during storage capacity expansion <br /> efforts. <br /> • EMP 9a-d: The impoundment volume and spillways are stated to need upgrades. The four spillways <br /> were redesigned. However, the impoundment volume will not need an upgrade because Knight Piesold <br /> has designed a new diversion channel, denoted as DC-EMP8a, that will divert runoff from the upper <br /> part of the existing contributing area for EMP 9a-d to EMP 8a instead (reference Figures 3.1 and 3.2). <br /> This channel will reduce the contributing area to EMP 9a-d such that its existing capacity will be <br /> sufficient and will increase the contributing area to EMP 8a, which is more amenable to expansion. <br /> • EMP 11: The impoundment volume and spillway are stated to need upgrades. However, CC&V has <br /> decided to reclassify this structure as a 'non-EMP' structure because it does not fit the definition or <br /> purpose of an 'EMP' at the mine. It is located in a depression above the Arequa Gulch VLF, not at the <br /> perimeter of the mining infrastructure. Furthermore, the existing capacity is sufficient to store the runoff <br /> volume from a single 10-year/24-hour storm event, and voids in this area could pose a safety hazard <br /> during expansion efforts. CC&V will regularly monitor the sediment accumulation within this structure <br /> and perform sediment removal efforts as often as necessary to maintain adequate storage for the runoff <br /> volume associated with a single 10-year/24-hour storm event. Further analyses were not performed for <br /> this structure and it is marked as not requiring upgrades, including the impoundment and spillway. <br /> The modified EMP and diversion channel basin delineations are presented on Figures 3.1 and 3.2, <br /> respectively. The updated analyses for the modified designs, which were presented to CC&V in the <br /> design report, account for modifications to the hydrologic analyses (e.g., contributing areas, CNs, routing <br /> parameters, models, etc.) and hydraulic analyses. By way of summary, Table 3.1 presents the design <br /> upgrade concepts that were completed by Knight Piesold. This table can be directly compared to the <br /> original evaluation presented in Table 2.9 to identify the changes described in this section. <br /> 4.0 EMP 22 DESIGN UPGRADES <br /> This section presents the civil design upgrades that were completed for EMP 22. The total impoundment <br /> volume was increased to comply with the storage design criterion via the addition of a second <br /> impoundment downstream of the existing impoundment. This required the design of two new spillways; <br /> one to connect the two impoundments and one to discharge flows to the downstream environment. <br /> 4.1 Hydrologic c Analyses <br /> The hydrologic analyses methodologies and associated input parameters that were used are described in <br /> Section 2.3. The results of the analyses to estimate 2x the runoff volume generated from the <br /> 10-year/24-hour storm event per the storage design criterion are presented in Table 2.7. The required <br /> storage volume for EMP 22 is approximately 37,300 cubic feet(ft3). <br /> The HEC-HMS hydrologic model flow routing diagram and peak flow results for the spillways are <br /> presented on Figure 4.1 and in Table 4.1, respectively. The following 100-year/24-hour storm event peak <br /> flows were estimated: <br /> • Inflow to impoundment no. 1: 11.7 cubic feet per second(cfs) <br /> • Outflow from impoundment no. 1 to impoundment no. 2(i.e., spillway no. 1): 11.0 cfs <br /> • Outflow from impoundment no. 2 to downstream environment(i.e., spillway no. 2): 10.5 cfs <br /> The latter two flows were applied as inputs to the hydraulic design analyses, which are presented in the <br /> following section. <br /> 9 <br />