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
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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
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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
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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
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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%
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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?
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DIAVIK WASTE ROCK PROJECT
Carbon Data
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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 (%)
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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
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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)
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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 (%)
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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
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DIAVIK WASTE ROCK PROJECT
Metal Release Focus (Mass Balance Graphs)
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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 (%)
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DIAVIK WASTE ROCK PROJECT
Metal Release Focus (Optical Mineralogy)
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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
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DIAVIK WASTE ROCK PROJECT
Metal Release Focus (µ-XRF)
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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
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DIAVIK WASTE ROCK PROJECT
Steel Fragment Contamination
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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
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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
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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)
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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
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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