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<br />Brooklyn Lower 0.86 20 60 110 0.6 9 672 122 105 <br />Mineral Creek Total 7 1,684 11.5 142 23,888 1,095 1,135 <br />Animas above Eureka <br />Ben Butler 0.34 40 300 28 0.8 8 225 1 165 <br />Silver wing 1.21 50 60 98 1.0 123 393 172 131 <br />Tom Moore 0.19 90 60 15 0.3 1 8 43 73 <br />Ea_le O.G7 9G 60 1 0.1 1 0 7 I8 <br />Luck~° Ja:,k 0.70 90 60 16 0.6 3 14 32 95 <br />Animas above Eureka Total 3 157 2.8 136 639 256 482 <br />Animas below Eureka <br />Clippea 0.09 90 60 6 0.2 7 80 57 70 <br />ButTato Bo1- 0.38 90 60 17 0.8 24 13 73 141 <br />Ben Franklin 0.37 90 60 81 0.4 13 612 99 95 <br />Caledonia 0.5 7 30 60 23 1.0 1~ 1 50 255 <br />Sunn~•side 2.50 90 1,000 40 2.3 10 0 536 664 <br />Animas below Eureka Total 4 168 4.6 69 706 815 1,224 <br />GRAND TOTAL 22 3,219 102 1,691 55,655 2,167 16,595 <br />V. REMEDIATION SCENARIOS <br />Using the characterization and ranking of sites, the effects of remediating multiple <br />sites can be estimated. This chapter compares several different remediation scenarios <br />including costs. The scenarios help determine what metal loading may be "reversible" <br />versus "irreversible". Natural sources of metals are considered 'irreversible. Some <br />human-related sources could also be called irreversible if they are very difficult and <br />expensive to change. There is the issue of how cost-effective these changes may be and <br />whether or not they would have a noticeable impact in protecting aquatic life. <br />Figures 8.18 to 8.21 of the Animas UAA show the levels of Al, Cd, Cu, Fe, Mn, <br />and Zn from adits and mine waste. These figures show the maximum amount of each of <br />the six metals that has been identified with mining-related activities. Most remediation <br />methods will remove only a portion of these metal loads. <br />Section III of this plan discussed the methodology that was used to rank and <br />prioritize specific adits and mine waste piles in the Basin, and discussed relevarn <br />technology that could be used to remediate those sources. Cost estimates and amount of <br />reduction corresponding to different technologies are comparable to the actual <br />remediation costs already encountered by SGC, the ARSG, and others in the Basin. (See <br />Chapter 3, Table 3.1 of the UAA). <br />The ARSG technical work group estimated the potential reductions in loading (as <br />a percentage reduction) that could be achieved by implementing remediation technologies <br />at each adit and mine waste site. Estimated loads contributed by each of 174 adits and <br />158 waste rock sites are shown in Appendix 11A of the UAA. Of those sites, load <br />reductions, applicable treatment technology, remediation option recommendations and <br />cost estimates have been derived for 78 adits and 127 mine waste sites. Those sites that <br />were not included contributed negligible loading, are a substantial distance from streams, <br />and «•ould not be cost-effective to remediate. <br />20 <br />