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BIG FIVE TUNNEL: A GEOTECHNICAL ENGINEERING EVALUATION WAS CONDUCTED ON TWO MINE WASTE ROCK <br />PILES (ONE ON THE NORTH SIDE OF CLEAR CREEK AND ONE ON THE SOUTH SIDE) CREATED FROM MATERIAL <br />EXCAVATED FROM THE BIG FIVE TUNNEL. THE CONCLUSIONS OF THESE EVALUATIONS INCLUDED: <br />• THE EASTERN PORTION OF THE WASTE ROCK PILE ON THE NORTH SIDE OF CLEAR CREEK AND THE <br />WESTERN PORTION OF THE WASTE ROCK PILE ON THE SOUTH SIDE OF CLEAR CREEK ARE <br />MARGINALLY STABLE TO UNSTABLE; <br />A 100-YEAR FLOOD COULD ERODE THE TOE OF EXISTING SLOPES BACK SEVEN TO TEN FEET AND <br />DECREASE SLOPE STABILITY. A 500-YEAR FLOOD COULD ERODE THE SLOPE BACK AN ADDITIONAL <br />TWO FEET; AND, <br />ALL SLOPES ARE SUBJECT TO EROSION IF LEFT EXPOSED. <br />BASED ON THE RESULTS OF THE GEOTECHNICAL INVESTIGATIONS, VOLUMES OF MARGINALLY STABLE AND <br />UNSTABLE MINE WASTE ROCK HAVE BEEN CALCULATED TO BE 2000 AND 6200 CY FOR THE NORTH AND SOUTH <br />BANKS, RESPECTIVELY. IN ADDITION, THE VOLUMES OF WASTE ROCK WHICH COULD BECOME MARGINALLY <br />STABLE OR UNSTABLE AFTER SEVEN TO TEN FEET EROSION BACK FROM THE TOE OF THE EXISTING WASTE PILES <br />DUE TO A 100-YEAR FLOOD WERE ALSO DETERMINED. THE VOLUME WAS CALCULATED TO BE 7200 AND 7900 CY <br />FOR THE NORTH AND SOUTH BANKS, RESPECTIVELY. <br />QUARTZ HILL AND NATIONAL TUNNEL: THE WASTE ROCK PILE ADJACENT TO THE NATIONAL TUNNEL IS <br />CONSIDERED STABLE. SOME SLOPES NEAR THE QUARTZ HILL TUNNEL ARE MARGINALLY STABLE AND SOME MINOR <br />RECONTOURING IS RECOMMENDED. <br />GREGORY INCLINE: IN 1987, THE TAILINGS PILE AT THE GREGORY INCLINE WAS RECONTOURED TO A 2:1 <br />(HORIZONTAL TO VERTICAL) SLOPE AND A GABION-BASKET RETAINING WALL WAS CONSTRUCTED. THE <br />GABION-BASKET WALL IS PARTIALLY IMMERSED IN CREEK WATER AND IS EXPOSED TO ACID DRAINAGE. <br />WITHOUT MAINTENANCE, THE WALL HAS AN ESTIMATED LIFE OF FIVE YEARS. THE WALL IS SUPPORTING AN <br />ESTIMATED 1,100 CUBIC YARDS OF TAILINGS WHICH WOULD OTHERWISE COLLAPSE INTO NORTH CLEAR CREEK. <br />WE DETAILS ON THE GEOTECHNICAL EVALUATIONS CONDUCTED AT THE CLEAR CREEK/CENTRAL CITY SUPERFUND <br />SITE CAN BE FOUND IN SECTION 8 OF THE REMEDIAL INVESTIGATION REPORT AND SECTION 5 OF THE <br />ADDENDUM TO THE REMEDIAL INVESTIGATION REPORT. <br />ESTIMATED IMPACT DUE TO CATASTROPHIC COLLAPSE: <br />A COMPUTER MODEL WAS USED TO PREDICT WATER QUALITY IN CLEAR CREEK AND NORTH CLEAR CREEK IN THE <br />ASSESSMENT OF HUMAN HEALTH AND ENVIRONMENTAL IMPACTS RESULTING FROM THE CATASTROPHIC FAILURE OF <br />THE BIG FIVE TUNNEL AND GREGORY INCLINE WASTE ROCK AND TAILINGS PILES. THE COLLAPSE OF THE BIG <br />FIVE WASTE ROCK PILES WAS MODELED UNDER REALISTIC, WORST CASE CONDITIONS. IN PARTICULAR, A <br />TOTAL OF 8,200 CUBIC YARDS OF MATERIAL (BOTH NORTH AND SOUTH BANKS COLLAPSE) WAS INSTANTANEOUSLY <br />INTRODUCED INTO CLEAR CREEK DURING NORMAL LOW FLOW (40 CUBIC FEET PER SECOND (CFS)). THE 8,200 <br />CUBIC YARDS IS THE QUANTITY OF MATERIAL CURRENTLY UNSTABLE AND WHICH COULD COLLAPSE INTO CLEAR <br />CREEK AT ANY TIME, INCLUDING DURING LOW FLOW CONDITIONS. ZINC AND ALUMINUM WERE SELECTED TO <br />REPRESENT THE VARIETY OF GEOCHEMICAL BEHAVIOR EXPECTED FROM THE TWELVE IDENTIFIED CONTAMINANTS <br />OF CONCERN. ARSENIC WAS NOT MODELED BECAUSE MEASURED CONCENTRATIONS IN THE STREAMS AND <br />LEACHATES WERE BELOW DETECTION LIMITS. LEAD AND COPPER WERE NOT MODELED BECAUSE LEACHATE <br />CONCENTRATIONS WERE LOW. <br />A COLLAPSE OF THE BIG FIVE PILE INTO CLEAR CREEK WOULD RESULT IN A PEAK DISSOLVED CONCENTRATION <br />OF 1,000 UG/L OF ALUMINUM AT THE POINT OF COLLAPSE. AFTER ONE DAY, THE CONTAMINATION WOULD <br />REACH GOLDEN WHERE A MAXIMUM CONCENTRATION OF 730 UG/L OF ALUMINUM IS PREDICTED. THE ALUMINUM <br />CONCENTRATION AT GOLDEN UNDER AMBIENT CONDITIONS IS 200 UG/L. A COLLAPSE OF THE BIG FIVE PILE <br />WOULD RESULT IN A MAXIMUM DISSOLVED CONCENTRATION OF 1,100 UG/L OF ZINC AT THE COLLAPSE POINT, <br />AN INCREASE FROM 400 UG/L OF ZINC UNDER AMBIENT CONDITIONS. THIS TRANSLATES INTO A MAXIMUM <br />CONCENTRATION OF 960 UG/L OF ZINC AT GOLDEN AFTER TWO DAYS WHICH WOULD GRADUALLY DECREASE TO 400 <br />0 / /L AFTER EIGHT DAYS. THE ZINC CONCENTRATION AT GOLDEN UNDER AMBIENT CONDITIONS IS ABOUT 300 <br />L. THE MODELING RESULTS INDICATE THAT MAXIMUM CONCENTRATIONS OF ALUMINUM AND ZINC WOULD <br />EXCEED AWQC IN ALL STREAM SEGMENTS DOWN TO GOLDEN. AT GOLDEN, THE AWQC WOULD BE EXCEEDED BY A <br />FACTOR OF 24 AND 89, RESPECTIVELY FOR ALUMINUM AND ZINC. BASED ON THE MODELING OF ZINC AND <br />ALUMINUM, IT IS ESTIMATED THAT CONCENTRATIONS OF SELECTED PARAMETERS IN CLEAR CREEK AT GOLDEN <br />WOULD ALSO EXCEED MAXIMUM CONTAMINANT LEVELS (MCLS) ESTABLISHED UNDER THE SAFE DRINKING WATER