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Diavik Waste Rock ProjectDiavik Waste Rock Project
MEND
Diavik Test Piles Group
Meeting
Project Update:
Tonalite
Dr. Peter Nason (Postdoctoral Fellow)
panason@uwaterloo.ca
UW: Saturday 7th November 2015
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Content Of Presentation
 Project Update
 Experimental Tests Conducted/Planned
 New Static Test Data
 Carbonate Study Focus
 Metal Release Focus
 Suitability of Tonalite as an Alternative Cover Material
 Planned Publications
2
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
3
Project Update: Tonalite Used as Cover Material
Sourced from production of
the A21 Kimberlite Pipe
(2018+)
A21 Lake sediments:
Sealing Layer (0.5-1.0 m)
A21 Waste Rock (Tonalite):
Protective Cover (3m)
Utilisation: 2021-2023
Project Directions:
1. Limiting ARD Formation with an Alkaline-Generating Cover
2. Understand metal release, mobility, transport and attenuation processes
3. Interaction of Tonalite-derived constituents with underlying Type III waste rock
constituents over time in an Arctic-clime
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Experimental Tests Conducted/Planned
Aim 1: Targeting and Evaluating Carbonate Weathering Potential
» XRF, XRD, SEM
» Carbon-Sulphur
» Transmitted and Reflected Light Microscopy
» 80-week Humidity Cell Experimental Leachate Data
» PHREEQC Modelling: Calcium S.I.
Aim 2: Sulphide Weathering and Metal Mobility
» XRF, SEM
» μ-XRF
» Modified 7-step Sequential Extraction Procedure
» Carbon-Sulphur
» Transmitted and Reflected Light Microscopy
» 80-week Humidity Cell Experimental Leachate Data
» MPN and DNA-isolation
4
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
New Static Tests
Core used in New Experiments
HCE: Used Composites of three cores:
New Experiments: 1 Core
• NP:AP: 17.5 (NAG > 3)
• Paste pH: 10.10
• Fizz Test: None
• SulfideTotal: <0.01%
• SulfurTotal: 0.006%
5
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Carbon, Calcium and Carbonate Mineralogy
Static Tests indicated < 0.8 % CaCO3
Optical Transmitted Mineralogical Analysis indicated trace
dolomite in hydrothermally-emplaced veins (< 0.1%)
XRD Mineral Analysis: Ankerite (Dolomite) Ca(Fe,Mg,Mn)(CO3)2
Fresh Tonalite Carbon Content (n = 3): 0.34 ± 0.013 %
• Crystalline Quartz (60%), Albite (Na) and Anorthite (Ca) (30%)
• Muscovite in the form of sericitization (5%)
• K-Feldspar: orthoclase/microcline (5%)
• Conforms to a typical Tonalite Igneous Rock Geochemistry
We assume C-data = Carbonates – Graphite? Steel-contamination?
We assume Ca-data = Carbonates – Gypsum? Anorthite?
6
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Carbon Data
7
0 1 2 3 4 5 6 7 8
L1
L2
L3
Room Temperature Cell 1 Room Temperature Cell 2
Difference to Fresh Tonalite (%)
0 1 2 3 4 5 6 7 8
L1
L2
L3
Cold Temperature Cell 1 Cold Temperature Cell 2
Difference to Fresh Tonalite (%)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Indication of Carbonate Weathering
 Next: PHREEQC Modelling – Dolomite Weathering and Gypsum8
6
7
8
9
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: pH
Week
pH
0
20
40
60
80
100
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Calcium
Week
Concentration(mmol/L)
0
20
40
60
80
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Magnesium
Week
Concentration(mmol/L)
R² = 0.6089
0
10
20
30
40
50
0 20 40 60 80
Ca:Mg Ratio
Calcium (mmol/L)
Magnesium(mmol/L)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Dolomite Weathering
1. CaMg(CO3)2(s) = MgCO3(s) + Ca2+ + CO3
2-
2. MgCO3(s) = Mg2+ + CO3
2−
3. CaMg(CO3)2(s) + Mg2+ = Ca2+ + 2MgCO3(s)
 Dissolution is much slower than calcite – release over time
 Dissolution is not indicated by Alkalinity
 Dissolution is much slower is Mg and Ca dissolved in solution
9
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Alkalinity in the Leachate
10
0
5
10
15
20
25
30
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Alkalinity
Week
Concentration(mg/LCaCO3per100ml)
 Indicates Alkalinity is generated – possible Calcite Dissolution
 Dissolved Calcium and Alkalinity have some correlation
indicating Calcium may be released by both Dolomite
dissolution and some other process (Calcite Dissolution)
R² = 0.4044
R² = 0.5843
0
10
20
30
40
50
0 1 2 3 4
Calcium (mg/L)
Ca:Alkalinity Ratio (TR1 and TC1)
Alkalinity(mg/LCaCO3per100ml)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Calcium and Magnesium Retention
Mass Balance Calculations:
 Ca and Mg are relatively enriched compared to Mass Change
 This reflects immobility and retention
 Next: PHREEQC Modelling – Dolomite Weathering and Gypsum 11
0.00 100.00 200.00 300.00
Ca
Mg
TR1-L1
TR1-L3
TR1-L2
Element Mass Change (%)
0.00 100.00 200.00 300.00
Ca
Mg
TC1-L1
TC1-L3
TC1-L2
Element Mass Change (%)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Indication of Dolomite
• XRD Mineral Analysis: Ankerite (Dolomite)
Ca(Fe,Mg,Mn)(CO3)2
• Leachate Data Ca:Mg Ratio = Correlated Release
• Mg – Ca leachate data – plotted to have depleted after 160
weeks in both Cold and Room Temperature Experiments (3
years):
• Only other source of Mg – Chlorite and biotite weathering
• Biotite was present in low (<2%) concentrations in mineralogy
12
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Tonalite Mineralogy
• XRD and Optical Mineralogy confirm Rock Type: Tonalite
• Albite (NaAlSi3O8) – 30%
• Anorthite (CaAl2Si2O8) – 5%
• Quartz – 55%
• Microcline (KAlSi3O8) – 5%
• Orthoclase (KAlSi3O8) - <1%
• Muscovite/ Biotite – 5%
• Trace Dolomite (<1%)
• Sulphides (<0.1%)
13
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Metal Release Focus (Leachate)
14
 No indication of Sulfide Weathering
 Flush Effect from fine fraction
0
100
200
300
400
500
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Iron
Week
Concentration(µmol/L)
0
10
20
30
40
50
60
70
80
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Sulphate
Week
Concentration(mmol/L)
R² = 0.1628
0.0
10.0
20.0
30.0
40.0
50.0
0 200 400 600
Fe:SO4 Ratio
Fe (µmol/L)
Sulphate(mmol/L)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Metal Release Focus (Leachate)
15
0
50
100
150
200
250
300
350
400
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Copper
Week
Concentration(µmol/L)
0
1
2
3
4
5
6
7
8
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Chromium
Week
Concentration(µmol/L)
0
10
20
30
40
50
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Nickel
Week
Concentration(µmol/L)
0
100
200
300
400
500
600
0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80
TR1 vs TC1: Zinc
Week
Concentration(µmol/L)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Metal Release Focus (Mass Balance Graphs)
16
 Only As, Cr, and Zn released in this pH environment
 Cr as Chromate (CrO4
2-), Arsenic (V), Zn2+
-100 0 100 200 300
Ni
Pb
Cu
Cr
Zn
As
TR1-L1
TR1-L3
TR1-L2
Element Mass Change (%)
-100 0 100 200 300
Ni
Pb
Cu
Cr
Zn
As
TC1-L1
TC1-L3
TC1-L2
Element Mass Change (%)
-100 -50 0 50 100
Fe
S
TR1-L1
TR1-L3
TR1-L2
Element Mass Change (%)
-100 -50 0 50 100
Fe
S
TC1-L1
TC1-L3
TC1-L2
Element Mass Change (%)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Metal Release Focus (Optical Mineralogy)
17
 Sulphides (Pyrite/Chalcopyrite/Sphalerite) are locked
inside mineral grains – not available to surface weathering
 Both Room and Cold: Sulphides Remain Un-altered in
SEM and optical mineralogical analysis
Fresh: In-situ Pyrite Room: In-situ Pyrite Cold: In-situ Pyrite
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Metal Release Focus (µ-XRF)
18
 Sulphides contain source of metals
 Weathered waste rock – Loss of Cu and Zn and Sulphur
 Spread of dissolved metals limited – pH controlled
 Retention of Zn elsewhere – mass balance – but also
largest concentrations (mmol) released in leachate
Fe Sulphur Cu Cr Pb Zn
Fresh
Room Tº
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Microbiology: MPN Enumerations
19
0.001 0.01 0.1 1 10 100 1000 10000
SOBa IOB SOBn
TR1-L2
TR1-L3
MPN/g
TR1-L1
0.001 0.01 0.1 1 10 100 1000 10000
SOBa IOB SOBnMPN/
Fresh Tonalite
0.001 0.01 0.1 1 10 100 1000 10000
SOBa IOB SOBn
TC1-L2
TC1-L3
MPN/g
TC1-L1
Fresh: Minimal Communities (<50 MPN/g)
Weathered: Both Temperatures:
• Low SOBa – supressed in Room Tº
• High (>2000 MPN/g) SOBn
• Moderate IOB ~ 240 MPN/g
• Reflects circum-neutral pH
• Low amounts of Iron and Sulphur
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Steel Fragment Contamination
20
 Optical and SEM indicate metal contamination from steel
fragments likely from drill core and/or crushing
 Samples were crushed and magnetically separated
 99% of metals grains were steel fragments
 Steel contains Fe, Mn, Cr, and Carbon, and other metals.
 No Sulphur is contained in these fragments
1 2 3 4 5 6 7 8 9 10
keV
0
1
2
3
4
5
6
7
8
cps/eV
FeFe Mn
Mn
Ni
Ni
ZnZn CdCd Si
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Sequential Extractions
 Modified 7-step Selective/Sequential Extraction procedure developed in-
house at University of Waterloo
 Currently: Ongoing – certifying the efficiency of Aqua Regia Step
 Can not compare other steps until Aqua Regia – Focus for rest of year
 Modification of Arrenhius Equation to calculate Dolomite Weathering
Step Fraction Target phase(s) Target description
1 Water soluble Soluble species Dissolution by simulated precipitation input (humidity cell
replication) and saturation—easily soluble ions
2 Exchangeable Weakly or non-specifically adsorbed
ions
Changes in the ionic composition or lowering of pH could
cause remobilisation of metals
3 Carbonates, less-
readily exchangeable
Specifically sorbed species Bound by covalent forces that require H+ or soft cation to
displace
4 Reducible Fe-amorphous to –crystalline minerals Primarily Fe(II)
5 Reducible Fe-crystalline minerals Unweathered and weathered Fe minerals, Fe(II) and
Fe(III)
6 Oxidizable Sulfides Available sulfides—pyrrhotite, chalcopyrite, pyrite,
sphalerite—with weathered coatings
7 Residual Residual non-silicate mineral Non-silicate and less resistant aluminosilicates
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Suitability of Tonalite as an Alternative Cover
 Minimal Release of Dissolved Metals
 Constituent Release Interaction with Frozen Core Over Time
 Mass Loading Calculations based on volume of Material
 Comparison with Type 1 material
Smith (2006)
Diavik Waste Rock Project
DIAVIK WASTE ROCK PROJECT
Planned Publications
1. Carbonate weathering potential of an inert
engineered cover material to alleviate acid
rock drainage formation in an unsaturated
waste rock pile in an Arctic clime
2. Developing novel laboratory-scale solutions to
evaluate sulphide-weathering evolution of a low-
sulphide containing waste rock
3. Environmental Engineered Tonalite Cover
interactions over a PAG – containing mine
waste rock pile in an Arctic Clime
23
Diavik Waste Rock ProjectDiavik Waste Rock Project
MEND
Diavik Test Piles Group
Meeting
Thank you for Listening
Dr. Peter Nason (Postdoctoral Fellow)
panason@uwaterloo.ca
UW: Saturday 7th November 2015

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UW_Diavik_Presentation_Nason (1)

  • 1. Diavik Waste Rock ProjectDiavik Waste Rock Project MEND Diavik Test Piles Group Meeting Project Update: Tonalite Dr. Peter Nason (Postdoctoral Fellow) panason@uwaterloo.ca UW: Saturday 7th November 2015
  • 2. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Content Of Presentation  Project Update  Experimental Tests Conducted/Planned  New Static Test Data  Carbonate Study Focus  Metal Release Focus  Suitability of Tonalite as an Alternative Cover Material  Planned Publications 2
  • 3. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT 3 Project Update: Tonalite Used as Cover Material Sourced from production of the A21 Kimberlite Pipe (2018+) A21 Lake sediments: Sealing Layer (0.5-1.0 m) A21 Waste Rock (Tonalite): Protective Cover (3m) Utilisation: 2021-2023 Project Directions: 1. Limiting ARD Formation with an Alkaline-Generating Cover 2. Understand metal release, mobility, transport and attenuation processes 3. Interaction of Tonalite-derived constituents with underlying Type III waste rock constituents over time in an Arctic-clime
  • 4. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Experimental Tests Conducted/Planned Aim 1: Targeting and Evaluating Carbonate Weathering Potential » XRF, XRD, SEM » Carbon-Sulphur » Transmitted and Reflected Light Microscopy » 80-week Humidity Cell Experimental Leachate Data » PHREEQC Modelling: Calcium S.I. Aim 2: Sulphide Weathering and Metal Mobility » XRF, SEM » μ-XRF » Modified 7-step Sequential Extraction Procedure » Carbon-Sulphur » Transmitted and Reflected Light Microscopy » 80-week Humidity Cell Experimental Leachate Data » MPN and DNA-isolation 4
  • 5. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT New Static Tests Core used in New Experiments HCE: Used Composites of three cores: New Experiments: 1 Core • NP:AP: 17.5 (NAG > 3) • Paste pH: 10.10 • Fizz Test: None • SulfideTotal: <0.01% • SulfurTotal: 0.006% 5
  • 6. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Carbon, Calcium and Carbonate Mineralogy Static Tests indicated < 0.8 % CaCO3 Optical Transmitted Mineralogical Analysis indicated trace dolomite in hydrothermally-emplaced veins (< 0.1%) XRD Mineral Analysis: Ankerite (Dolomite) Ca(Fe,Mg,Mn)(CO3)2 Fresh Tonalite Carbon Content (n = 3): 0.34 ± 0.013 % • Crystalline Quartz (60%), Albite (Na) and Anorthite (Ca) (30%) • Muscovite in the form of sericitization (5%) • K-Feldspar: orthoclase/microcline (5%) • Conforms to a typical Tonalite Igneous Rock Geochemistry We assume C-data = Carbonates – Graphite? Steel-contamination? We assume Ca-data = Carbonates – Gypsum? Anorthite? 6
  • 7. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Carbon Data 7 0 1 2 3 4 5 6 7 8 L1 L2 L3 Room Temperature Cell 1 Room Temperature Cell 2 Difference to Fresh Tonalite (%) 0 1 2 3 4 5 6 7 8 L1 L2 L3 Cold Temperature Cell 1 Cold Temperature Cell 2 Difference to Fresh Tonalite (%)
  • 8. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Indication of Carbonate Weathering  Next: PHREEQC Modelling – Dolomite Weathering and Gypsum8 6 7 8 9 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: pH Week pH 0 20 40 60 80 100 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Calcium Week Concentration(mmol/L) 0 20 40 60 80 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Magnesium Week Concentration(mmol/L) R² = 0.6089 0 10 20 30 40 50 0 20 40 60 80 Ca:Mg Ratio Calcium (mmol/L) Magnesium(mmol/L)
  • 9. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Dolomite Weathering 1. CaMg(CO3)2(s) = MgCO3(s) + Ca2+ + CO3 2- 2. MgCO3(s) = Mg2+ + CO3 2− 3. CaMg(CO3)2(s) + Mg2+ = Ca2+ + 2MgCO3(s)  Dissolution is much slower than calcite – release over time  Dissolution is not indicated by Alkalinity  Dissolution is much slower is Mg and Ca dissolved in solution 9
  • 10. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Alkalinity in the Leachate 10 0 5 10 15 20 25 30 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Alkalinity Week Concentration(mg/LCaCO3per100ml)  Indicates Alkalinity is generated – possible Calcite Dissolution  Dissolved Calcium and Alkalinity have some correlation indicating Calcium may be released by both Dolomite dissolution and some other process (Calcite Dissolution) R² = 0.4044 R² = 0.5843 0 10 20 30 40 50 0 1 2 3 4 Calcium (mg/L) Ca:Alkalinity Ratio (TR1 and TC1) Alkalinity(mg/LCaCO3per100ml)
  • 11. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Calcium and Magnesium Retention Mass Balance Calculations:  Ca and Mg are relatively enriched compared to Mass Change  This reflects immobility and retention  Next: PHREEQC Modelling – Dolomite Weathering and Gypsum 11 0.00 100.00 200.00 300.00 Ca Mg TR1-L1 TR1-L3 TR1-L2 Element Mass Change (%) 0.00 100.00 200.00 300.00 Ca Mg TC1-L1 TC1-L3 TC1-L2 Element Mass Change (%)
  • 12. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Indication of Dolomite • XRD Mineral Analysis: Ankerite (Dolomite) Ca(Fe,Mg,Mn)(CO3)2 • Leachate Data Ca:Mg Ratio = Correlated Release • Mg – Ca leachate data – plotted to have depleted after 160 weeks in both Cold and Room Temperature Experiments (3 years): • Only other source of Mg – Chlorite and biotite weathering • Biotite was present in low (<2%) concentrations in mineralogy 12
  • 13. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Tonalite Mineralogy • XRD and Optical Mineralogy confirm Rock Type: Tonalite • Albite (NaAlSi3O8) – 30% • Anorthite (CaAl2Si2O8) – 5% • Quartz – 55% • Microcline (KAlSi3O8) – 5% • Orthoclase (KAlSi3O8) - <1% • Muscovite/ Biotite – 5% • Trace Dolomite (<1%) • Sulphides (<0.1%) 13
  • 14. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Metal Release Focus (Leachate) 14  No indication of Sulfide Weathering  Flush Effect from fine fraction 0 100 200 300 400 500 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Iron Week Concentration(µmol/L) 0 10 20 30 40 50 60 70 80 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Sulphate Week Concentration(mmol/L) R² = 0.1628 0.0 10.0 20.0 30.0 40.0 50.0 0 200 400 600 Fe:SO4 Ratio Fe (µmol/L) Sulphate(mmol/L)
  • 15. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Metal Release Focus (Leachate) 15 0 50 100 150 200 250 300 350 400 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Copper Week Concentration(µmol/L) 0 1 2 3 4 5 6 7 8 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Chromium Week Concentration(µmol/L) 0 10 20 30 40 50 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Nickel Week Concentration(µmol/L) 0 100 200 300 400 500 600 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 TR1 vs TC1: Zinc Week Concentration(µmol/L)
  • 16. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Metal Release Focus (Mass Balance Graphs) 16  Only As, Cr, and Zn released in this pH environment  Cr as Chromate (CrO4 2-), Arsenic (V), Zn2+ -100 0 100 200 300 Ni Pb Cu Cr Zn As TR1-L1 TR1-L3 TR1-L2 Element Mass Change (%) -100 0 100 200 300 Ni Pb Cu Cr Zn As TC1-L1 TC1-L3 TC1-L2 Element Mass Change (%) -100 -50 0 50 100 Fe S TR1-L1 TR1-L3 TR1-L2 Element Mass Change (%) -100 -50 0 50 100 Fe S TC1-L1 TC1-L3 TC1-L2 Element Mass Change (%)
  • 17. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Metal Release Focus (Optical Mineralogy) 17  Sulphides (Pyrite/Chalcopyrite/Sphalerite) are locked inside mineral grains – not available to surface weathering  Both Room and Cold: Sulphides Remain Un-altered in SEM and optical mineralogical analysis Fresh: In-situ Pyrite Room: In-situ Pyrite Cold: In-situ Pyrite
  • 18. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Metal Release Focus (µ-XRF) 18  Sulphides contain source of metals  Weathered waste rock – Loss of Cu and Zn and Sulphur  Spread of dissolved metals limited – pH controlled  Retention of Zn elsewhere – mass balance – but also largest concentrations (mmol) released in leachate Fe Sulphur Cu Cr Pb Zn Fresh Room Tº
  • 19. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Microbiology: MPN Enumerations 19 0.001 0.01 0.1 1 10 100 1000 10000 SOBa IOB SOBn TR1-L2 TR1-L3 MPN/g TR1-L1 0.001 0.01 0.1 1 10 100 1000 10000 SOBa IOB SOBnMPN/ Fresh Tonalite 0.001 0.01 0.1 1 10 100 1000 10000 SOBa IOB SOBn TC1-L2 TC1-L3 MPN/g TC1-L1 Fresh: Minimal Communities (<50 MPN/g) Weathered: Both Temperatures: • Low SOBa – supressed in Room Tº • High (>2000 MPN/g) SOBn • Moderate IOB ~ 240 MPN/g • Reflects circum-neutral pH • Low amounts of Iron and Sulphur
  • 20. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Steel Fragment Contamination 20  Optical and SEM indicate metal contamination from steel fragments likely from drill core and/or crushing  Samples were crushed and magnetically separated  99% of metals grains were steel fragments  Steel contains Fe, Mn, Cr, and Carbon, and other metals.  No Sulphur is contained in these fragments 1 2 3 4 5 6 7 8 9 10 keV 0 1 2 3 4 5 6 7 8 cps/eV FeFe Mn Mn Ni Ni ZnZn CdCd Si
  • 21. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Sequential Extractions  Modified 7-step Selective/Sequential Extraction procedure developed in- house at University of Waterloo  Currently: Ongoing – certifying the efficiency of Aqua Regia Step  Can not compare other steps until Aqua Regia – Focus for rest of year  Modification of Arrenhius Equation to calculate Dolomite Weathering Step Fraction Target phase(s) Target description 1 Water soluble Soluble species Dissolution by simulated precipitation input (humidity cell replication) and saturation—easily soluble ions 2 Exchangeable Weakly or non-specifically adsorbed ions Changes in the ionic composition or lowering of pH could cause remobilisation of metals 3 Carbonates, less- readily exchangeable Specifically sorbed species Bound by covalent forces that require H+ or soft cation to displace 4 Reducible Fe-amorphous to –crystalline minerals Primarily Fe(II) 5 Reducible Fe-crystalline minerals Unweathered and weathered Fe minerals, Fe(II) and Fe(III) 6 Oxidizable Sulfides Available sulfides—pyrrhotite, chalcopyrite, pyrite, sphalerite—with weathered coatings 7 Residual Residual non-silicate mineral Non-silicate and less resistant aluminosilicates
  • 22. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Suitability of Tonalite as an Alternative Cover  Minimal Release of Dissolved Metals  Constituent Release Interaction with Frozen Core Over Time  Mass Loading Calculations based on volume of Material  Comparison with Type 1 material Smith (2006)
  • 23. Diavik Waste Rock Project DIAVIK WASTE ROCK PROJECT Planned Publications 1. Carbonate weathering potential of an inert engineered cover material to alleviate acid rock drainage formation in an unsaturated waste rock pile in an Arctic clime 2. Developing novel laboratory-scale solutions to evaluate sulphide-weathering evolution of a low- sulphide containing waste rock 3. Environmental Engineered Tonalite Cover interactions over a PAG – containing mine waste rock pile in an Arctic Clime 23
  • 24. Diavik Waste Rock ProjectDiavik Waste Rock Project MEND Diavik Test Piles Group Meeting Thank you for Listening Dr. Peter Nason (Postdoctoral Fellow) panason@uwaterloo.ca UW: Saturday 7th November 2015