NM Water Resources Research Institute Environmental Conditions of the Animas and San Juan Watersheds with Emphasis on Gold King Mine
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1 The Gold King Mine Spill in the Context of Historical Water Quality Impacts to Utah s San Juan River and Lake Powell NM Water Resources Research Institute Environmental Conditions of the Animas and San Juan Watersheds with Emphasis on Gold King Mine June 20, 2017 Henderson Fine Arts Center, San Juan College Christopher L. Shope, Ph.D. Utah Department of Environmental Quality
2 Monitoring and Sampling Locations Event Based GKM Event & Long-Term Sampling Locations 2
3 Monitoring and Sampling Locations - Historical Historical Sampling Locations
4 Utah Screening Results Water Column Aquatic Life Use (Dissolved Metals) No Exceedence Above Screening Level Prior to Plume Arrival Estimated Plume Arrival Post Plume Arrival Monitoring Location Aluminum Antimony Arsenic Barium Beryllium Cadmium Chromium Utah Aquatic Life Use 1-hour Utah Aquatic Life Use 4-hour Collection Collection Site Description Date Time ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l 8/8/2015 1:23 PM 47, :02 PM 33, /9/2015 3:05 PM 26,700 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 6:00 PM 24,600 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 9:02 PM 31, /10/2015 9:11 AM 39, :06 PM 43, /11/2015 8:50 AM 77, , :17 PM 56, /12/2015 9:50 AM 31, :09 PM 28, /13/ :01 AM 38, /14/2015 8:50 AM 44, /15/2015 9:43 AM 14, /16/2015 9:15 AM 9, /18/2015 9:56 AM 3, /19/2015 9:30 AM 4, /20/2015 9:44 AM 3, /24/2015 3:10 PM 1, /25/2015 3:30 PM 1, /26/2015 2:50 PM 1, /27/2015 3:40 PM 117, /28/2015 4:25 PM 196, , /23/2015 6:30 PM 5, /2/ ,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/15/ :00 PM 34,400 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/18/ ,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 12:00 AM 23,900 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/19/2015 San Juan 166,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 12:00 PM US160 Xing in CO 248,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/20/ :01 AM 202,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/21/ :00 AM 230,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/22/ :00 PM 94,800 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/23/ :00 AM 138,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 12:00 PM 189,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 2/16/2016 3:00 PM 70, /23/ :10 AM 2, /29/2016 4:00 PM 3, /9/2016 2, :20 AM 3/15/2016 1, /22/2016 9:30 AM /28/2016 4:50 PM /4/ :20 PM 1, , /12/2016 2:00 PM /19/ :25 PM 2, /26/ :45 AM 3, /2/2016 2:00 PM 6, /9/ :30 PM 1, /15/ :15 PM 13, /21/2016 3:30 PM 22, /31/2016 4:15 PM 3, /5/ :30 AM 4, /13/ :30 PM 2, /18/2016 3:30 PM 2, /25/2016 2:45 PM 1,655 7/4/ :45 AM 8, /9/2016 2:45 PM 1, Locations on the San Juan River MLID San Juan R at US160Xing in CO MLID San Juan R at Town of Montezuma MLID San Juan R at Sand Island MLID San Juan R at Mexican Hat US163 Xing MLID San Juan R at Clay Hills boat ramp Cobalt Copper Iron Lead Manganese Mercury Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc 4
5 Utah Screening Results Summary San Aquatic Juan Life Use River (Dissolved and Metals) tributary locations MLID San Juan R at US160Xing in CO MLID San Juan R at Town of Montezuma MLID San Juan R at Sand Island No Exceedence Above Screening Level Prior to Plume Arrival Estimated Plume Arrival Post Plume Arrival Aluminum Antimony Arsenic Barium Beryllium Cadmium Utah Aquatic Life Use 1-hour Utah Aquatic Life Use 4-hour MLID San Juan R at Mexican Hat US163 Xing Monitoring Collection Collection ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l ug/l Location Site Description Date Time MLID San 8/8/2015 Juan 1:23 PM R at 47,400 Clay 0.5 Hills 1.3boat ramp :02 PM 33, :05 PM 26,700 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS MLID McElmo 8/9/2015 Cr at U262 Xing near Town of Montezuma 6:00 PM 24,600 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 9:02 PM 31, MLID Montezuma 9:11 AM Cr 39,900at U Xing /10/2015 2:06 PM 43, /11/2015 8/12/2015 8:50 AM 9:50 AM 77,000 31, , :17 PM 12:09 PM 56,900 28, /13/ :01 AM 38, /14/2015 8:50 AM 44, /15/2015 9:43 AM 14, /16/2015 9:15 AM 9, /18/2015 9:56 AM 3, /19/2015 9:30 AM 4, /20/2015 9:44 AM 3, /24/2015 3:10 PM 1, /25/2015 3:30 PM 1, /26/2015 2:50 PM 1, /27/2015 3:40 PM 117, /28/2015 4:25 PM 196, , /23/2015 6:30 PM 5, /2/ ,000 NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 10/1 / PM Standard / Benchmark Phase 1 Exceedances Phase 2 Exceedances 1C Domestic Water 1 (Pb) 0 3B Aquatic Life 4 Agricultural Chromium Cobalt 16 (Cd, Cu, Fe, Pb, Zn) 149 (Al) 6 (Al, Fe, Mn) 2 (TDS) Copper Iron Lead Manganese Mercury Molybdenum Nickel Selenium Silver 126 (Al) 1 (Mo) 24 (TDS) Recreational Screening 0 0 Sediment Screening 6 (Mg, Se) in SJR 101 (Al), 2 (Fe) cores 19 (Al), 1 (As, Pb), 5 (Mn) - sed traps 0 Thallium Vanadium Zinc 5
6 Utah San Juan River Metal Concentration Analyte concentration generally decreased downstream (cool to warm colors) Some elements (Al, Pb, Zn) show GKM highs, although others in historical range. 6
7 System Concentration Gradients Evaluate concentrations over entire system GKM through Lake Powell 7
8 Utah San Juan River Metal Loading 8
9 USGS Cores and Sediment Traps in Lake Powell 9
10 2010 USGS Sediment Cores in San Juan R. Delta Aquatic Life Screening Value Exceedances Exceedances of Al, As, Cr, Cu, Fe, Pb, Mn, Ni, Zn Across all 3 cores and at multiple depths 10
11 2010 USGS Sediment Cores in San Juan R. Delta Again, this includes more analytes Change in ratio suggests different source/process Some deviations but not significant change typically As, Cd, Zn, Zr, Pb, Bi, Cu, Mo, Sb, U show high ratio deviation ~ 1.2 m. Na, Se, Ba, Tl show higher ratio values > 1.2 m Alternatively, Fe, V, Co, Ni, Sn, W, Mg, Cr, Cs, Cu all show lower ratios > 1.2 m Analyte vs Al ratio at each depth interval for the upstream core 11
12 USGS Sediment Traps in Lake Powell Delta Three sediment trap periods at three separate locations (Up-, mid-, down-stream) Analysis complicated by monsoonal storms 12
13 Potential for Source Identification UDEQ funding efforts to identify relative importance of natural and mining sources in basin Different elemental contributions from different geologic sources (e.g., Mancos Shale) Isotopic and ion ratio fingerprinting of sources 13
14 Potential for Source Identification UDEQ funding efforts to identify relative importance of natural and mining sources in basin Different elemental contributions from different geologic sources (e.g., Mancos Shale) Isotopic and ion ratio fingerprinting of sources 14
15 Acid Mine Drainage Strategy for Utah 15
16 Acid Mine Drainage Strategy for Utah Management of abandoned mine reclamation delegated to State with Federal oversite. Abandoned Mines are considered mines abandoned before Utah is one of the highest mineral producing states (Bingham Canyon) Since 1983, many AML reclamations in Utah with over 5,500 mine closures. 5 standard procedures for mine closures; backfilling dry mineshafts is most common in the State of Utah. Currently no large-scale / statewide efforts to address mine drainage in Utah. Landowners liable for mines, including safety and reclamation of those mines. Many mines of concern are on private land. In response to GKM: mine openings identified across Utah 2267 mine features inventoried. 29 mines found with significant discharge Site visits to 19 mines in mines have significant flow into perennial streams 3 mines are flooded, backfilled locations with no oversight (similar to GKM) 16
17 Thank you Questions? Christopher L. Shope, Ph.D. Utah Dept. of Env. Quality Div. of Water Quality
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