field studies to assess biostim ulation for rem ediation
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Field Studies to Assess Biostim ulation for Rem ediation of Radionuclides and Heavy Metals at an in situ Leach Mine Site J o h n W i l l f o r d , K e v i n Ch a m b e r l a i n , P a u l R e i m u s , a n d J i m Cl a y Co l l a b o r a


  1. Field Studies to Assess Biostim ulation for Rem ediation of Radionuclides and Heavy Metals at an in situ Leach Mine Site J o h n W i l l f o r d , K e v i n Ch a m b e r l a i n , P a u l R e i m u s , a n d J i m Cl a y Co l l a b o r a t o r s : Cr a i g Co o k , P e t e r S t a h l , S e a n S c o t t , Ca l v i n S t r o m , D a v i d W i l l i a m s , L a w r e n c e R e i m a n n , Ca r l v a n d e r L i n d e n , K e n W i l l i a m s , J o y c e M c B e t h , R i z l a n B e r n i e r - L a t m a n i

  2. Geology and Wellfield Development Groun ound Level Shale le Impervious Layer Overlyin lying Aquifer fer Shale le Impervious Layer Ore re Ore B e Bod ody Bear earing Aquifer fer Impervious Layer Shale le • The ore occurs at depths of several hundred feet, the extent is determined by surface drilling. • Ore is typically confined by impervious shale. • After deposit delineated, an extraction plan is prepared and grids of injection and production wells are installed.

  3. Uranium Extraction and To Ion Exchange Circuit Controlling Ground Water From Ion Exchange Movem ent Circuit w/ Oxygen & Carbon Dioxide Shale Overlying Aquifer Shale Ore Ore B e Bod ody Bearing Aquifer Shale Recovery Fluid Underlying Aquifer

  4. Traditional Restoration Strategies  Reverse Osmosis Water Sweeps  Remove extra mining lixiviant, TDS  Remove some Uranium (VI)  Chemical Treatments  Attempt to reestablish reducing environment  i.e. Hydrogen Sulfide or Sodium Sulfide  Very expensive, large consumptive water loss  Evidence of rebound after treatment-U not valence reduced  Can bio-stimulation improve the efficiency of restoration?

  5. Previous Smith Ranch Highland Trial Sugar Processing Waste Crude Soybean Oil Emulsified Vegetable Oil Acetate Acetate/ Yeast Extract Molasses Day 1 MeOH/ Molasses Day 15 Day 35 MeOH/ Molasses/ Yeast Extract Safflower Oil/ EtOH Cheese Whey PO4 No Add 0 2 4 6 8 10 12 14 16 Uranium Concentration (ppm) (Adapted from Hatzinger, 2004)

  6. Microcosm Experiment Objectives  Examine potential biostimulants for their efficacy in promoting biological reduction of Uranium (VI) in SRH system  Tryptone  Safflower oil with Methanol  Determine effective measurements to demonstrate biological reducing situations  Water chemistry analyses  Carbon-isotopic analyses  Uranium-isotopic analyses  Microbial community analyses

  7. Soluble Uranium Results 8.000 7.000 6.000 Uranium Concentration (m g/ L) 5.000 4.000 3.000 2.000 1.000 0.000 Day 1 Day 5 Day 10 Day 15 Day 20 Day 25 Day 30 Low No Add High No Add Low + tryp High + tryp Low + Saff High + Saff *53% reduction in Low + Tryp; 68% reduction in High + Tryp

  8. Evidence of Microbial Activity 1.6 45 40 1.4 Geobacter ug FA/ g ug FA/ g of Soil 35 1.2 30 1 25 0.8 20 0.6 15 0.4 10 0.2 5 0 0 1 10 15 20 25 30 0 10 20 30 40 Tim e in Days Tim e in Days High+Saff High+Tryp High NoAdd High+Saff High+Tryp High NoAdd Low+Saff Low+Tryp Low NoAdd Low+Saff Low+Tryp Low NoAdd Starting Sediment Geobacter spp. specific Fatty Acids CO3 Avg 15:0 iso; 16:1 w7c; 16:0 0.40 0.35 Reduced Oxidized 0.30 m g CO3 0.25 0.20 0.15 0.10 Day 1 Day 5 Day 10 Day 15 Day 20 Day 25 Day 30 High + Tryp Low + Tryp High + Saff Hydrogen Low + Saff High No Add Low No Add Sulfide Odor

  9. Uranium Isotope Analysis Methods  Isotopic fractionation correlates to valence reduction  Samples of monitoring waters  Sample load ~100 nanograms (10 -9 gm) U  Spiked with 233 U/ 236 U tracer  Purification on ion exchange columns  Sample/ blank ~10,000  Multi-collector, inductively-coupled plasma, mass spectrometry (MC-ICP-MS)

  10. U concentration and isotopic fractionation-High Tryptone

  11. Other Issues/ Unanswered Questions from Microcosm Study  How much tryptone is required to stimulate growth and reduction of uranium (VI)?  Where in mining process would this type of biostimulation be the most beneficial?  Do the monitoring metrics hold up in a continuous flow system?

  12. Column Study Design  Study was setup in a 4x4 system  4 levels of tryptone stimulation  2000 mg/ L  200 mg/ L  20 mg/ L  No tryptone control (No Add)  4 types of water  High TDS/ U (7-8 ppm U)  Medium TDS/ U (2-3 ppm U)  Low TDS/ U (~1 ppm U)  Deionized control  16 total columns – 4 per syringe pump

  13. Visually Observable Changes Oxidized Reduced *44.4 mL average pore volume

  14. Soluble Uranium Concentration Results

  15. 20 0 0 m g/ L Treatm ent  99.3% reduction in High 2000 treatment  Consistent reduction beginning at ~Day 42  Synchrotron data demonstrates high U(IV) presence in sediment 20 0 m g/ L Treatm ent  82.6% reduction in Medium 200 treatment Beginning at  ~Day 112  Despite initial reduction, clear rebound in High TDS/ U water

  16. Uranium/ Carbonate Concentrations

  17. Uranium Fractionation/ Concentrations

  18. Conclusions of Column Study  Tryptone was effective at promoting microbial growth and reduction of uranium in a continuous flow system  Clogging due to stimulation not observed  2ooo mg/ L of tryptone shown effective at 7-8 mg/ L uranium  200 mg/ L of tryptone shown effective at 2-3 mg/ L uranium  20 mg/ L did not display reduction different from No Add control  Monitoring metrics:  Carbonate concentration syncs well with uranium reduction activity  Uranium isotopic fractionations syncs well with uranium reduction activity  238 U/ 235 U fractionation very sensitive to changes in U concentration, including increases

  19. Field Trial Experiment Objectives  Evaluate tryptone for its ability to promote biological reduction of Uranium (VI) in a field situation  Continue monitoring metrics to determine effective measurements to demonstrate biological reducing situations  Water chemistry analyses  Carbon-isotopic/ carbonate analyses  Uranium-isotopic analyses  Microbial community analyses  Demonstrate biostimulation practicality  To ease some regulatory questions from previous efforts

  20. Field test for bio-stimulation

  21. FBA tracers well # 121 4I-213 (2,4) 3500 2.6 DFBA 3000 Concentrations (ug/L) PFBA 2500 4I-214 2.5 DFBA 4I-217 (2,6) 2000 (PFBA) 4P-121 2.4 DFBA 1500 1000 Core 500 0 4I-218 (2,5) 0 2 4 6 8 10 12 14 16 18 20 22 24 26 Days of Pumping since Start of Injection 4I-201 (2,6) FBA tracers well # 113 3000 2.6 DFBA 2500 PFBA Concentrations (ug/L) 4I-202 4I-206 2.5 DFBA 2000 (2,5) (2,4) 4P-113 2.4 DFBA 1500 1000 500 4I-207 (PFBA) 0 0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 Days of Pumping since Start of Injection

  22. Field Trial at SRH  Tryptone stimulation with longer-term monitoring in one field pattern in Mine Unit 4 at SRH  Stimulated P121 well pattern with tryptone P121 (~80 mg/ L)  200kg total  Well pattern P113 used as P113 control pattern  Tryptone added Sept- Oct 2014

  23. Measured Concentrations

  24. Uranium Fractionation Stimulation Begins

  25. Conclusions of Field Trial  Reducing environment:  Overall, data suggest a reducing environment in stimulated well pattern P121  Selenium & uranium concentrations decrease  Arsenic & iron (ferrous) concentrations increase  Uranium isotopic fractionation is significant in stimulated environment  Most recent data may suggest increased stability of reduced uranium in the stimulated pattern  More data necessary

  26. Field Trial Thoughts, Future Directions  Tryptone quantity added was likely too low  Only ~40% of the low value suggested based upon column data  Was this the proper point in restoration to bioremediate?  Didn’t clog any wells  In-lab studies show reduction at higher levels, plus bottom level in microcosms was close to 0.4ppm  What makes tryptone effective?  Carry-on lab trial is providing insight

  27. Acknowledgements  Cameco, Inc.  State of Wyoming Legislature, ISRU Technology Research Program  UW School of Energy Resources

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