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Ouray Silver Mines Inc. <br /> Technical Revision 15 May 24,2021 <br /> both piles would be stable and have an adequate safety factor as long as the proper compaction <br /> were achieved when the material was placed in the piles. This compaction requirement was 94% <br /> of the maximum dry density,as determined using ASTM D-698. The results of the 2015 slope <br /> stability analysis are presented in Appendix 3. The geotechnical work on tailings stability will be <br /> updated(once conditional approval is granted)with data from the tails generated by the upgraded <br /> mill to demonstrate stability of the TSFs. <br /> In 2017, feasibility-level metallurgical studies were conducted by FLSmidth. This program was <br /> conducted on variability composites that represented spatial and grade variations within the <br /> Virginius Main Vein,the Footwall Vein and the Yellow Rose Vein, as well as a master <br /> composite the was formulated to represent the weighted average contribution from these veins <br /> during the first five years of mining. Multi-element analyses were conducted on the final lead <br /> concentrate,zinc concentrate, and flotation tailings produced from Locked-cycle tests on the <br /> master composite and the results are presented in Table 5. A weighted tailings composite sample <br /> from the last 3 cycles was submitted for acid-base accounting(ABA)determination by <br /> McClelland Labs in Reno,Nevada and the results are summarized in Table 6. It was found that <br /> the flotation tailings had an acid generating potential(AGP)of 38.1 and an acid neutralizing <br /> potential(ANP)of 89.4,resulting in a net neutralizing potential(NNP)of 51.3 and an ANP/ANP <br /> ratio of 2.35. These results indicate that the flotation tailings are not acid generating. <br /> Ouray Silver Mines installed groundwater monitoring wells at the toe of the designated tailings <br /> embankments along Sneffels Creek as part of the approved DRMS permit. The groundwater that <br /> passes through the Revenue and Atlas waste pile areas is properly intercepted by the wells GW- <br /> 1,GW-2,and GW- 3. Each well location represents a pair of wells that are used to compare the <br /> water that might pass through any tailings with the water that is present in the porous rock below <br /> the original topsoil level. The (A)well in each location represents the background water,while <br /> the(B)well represents water that may have passed through the tailings. Well GW-3A was <br /> replaced b well GW-3R TR-10 to assist monitoring Pond#2. All wells were initially sampled <br /> P Y ( ) g Y p <br /> to establish a baseline. GW-IA and GE-1B were not sampled from August 2015 through August <br /> 2019 with DRMS permission because there had development there. Currently, all the wells are <br /> purged and sampled at least quarterly,with additional samples being taken as desired. The last 5 <br /> ears of water quality data can be found in Appendix 4. <br /> Y q tY pp <br /> Page 12 of 12 <br />