ML/ARD Impacts and Rehabilitation Planning for...
Transcript of ML/ARD Impacts and Rehabilitation Planning for...
ML/ARD Impacts and Rehabilitation Planning for Rum Jungle
November 28th, 2018 25th MEND ML/ARD Workshop
Paul Ferguson1, Christoph Wels1, David Jones2, Graham Farrer3
1Robertson GeoConsultants Inc. 2DR Jones Environmental Excellence
3NT Department of Primary Industry and Resources
Overview
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o Focus: “what happened, what was unexpected and future objectives”
o Initial rehabilitation in the 1980s • Works completed • Performance • Current site conditions
o Future rehabilitation plan • Preferred rehabilitation strategy • Predicted performance
o Summary and Path Forward
Site Location and Physical Setting
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Darwin
Rum Jungle Fog Bay (Finniss River)
Browns (C&M)
Rum Jungle
Markich and Jeffree (2002), The Finniss River: A Natural Laboratory of Mining Impacts – Past, Present, and Future, ANSTO E/748.
East Branch of Finniss River (no biota in 1960s and 1970s)
15 km
Timeline for Mining and Rehabilitation
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1949 Discovery of uranium
Active mining
1953 to 1971
1971 Site abandoned
1983 to 1985 Rum Jungle Rehabilitation Project (AU$16.2M)
2010 Rehabilitation planning re-commences
1986 to 1998 Monitoring Rehab /
• Uranium (for CDA) • Cu, Ni, and Co
Planning/C&M
1977 Limited rehabilitation
Historic Site Layout (1970s) – Prior to Rehabilitation
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Main WRD
Main Pit
Dyson’s Pit
Old Tailings Dam
Intermediate Pit
East Branch of the Finniss River (EBFR)
Dyson’s WRD
Intermediate WRD
Heap leach pile
Diversion channel
Mill
Post-Rehabilitation (Current) Site Layout
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pH 7 to 8 SO4 500 to 1,500 mg/L Low concentrations of Cu, Co, Ni, and Zn
Dyson’s Pit (backfilled)
Main WRD
(covered)
Dyson’s WRD (covered)
Int. WRD (covered)
Browns Pit
‘Old Tailings Dam’ area (tailings re-located to Dyson’s Pit)
Int. Pit (limed)
Main Pit (treated)
Former heap leach pile (spent material to Dyson’s Pit)
Rehabilitation Objectives (1983): 1. Achieve drinking water guidelines in EBFR 2. Reduce public health hazards (from radiation) 3. Improve site aesthetics, including re-vegetation
EBFR (Monitoring Station)
EFDC (90% of flows)
10%
Pre-Rehabilitation Conditions
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Copper heap leach pile, August 1984 Old Tailings Dam, June 1983
Main (White’s) WRD, June 1983 Intermediate WRD, January 1985
Post-Rehabilitation Conditions
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Copper heap leach pad, August 1986 Old Tailings Dam, May 1986
Main (White’s) WRD, May 1985 Intermediate WRD, May 1986
Current Site Conditions
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Main WRD and Fitch Creek Dyson’s Area
Intermediate WRD and EFDC
Conceptual cross-section, Dyson’s (backfilled) Pit
Vegetation Community Map (from EcoLogical, 2014)
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Invasive grasses, e.g. Gamba (Units 12 to 19, in orange)
Copper Concentrations in EBFR Downstream
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Before initial rehabilitation in 1984/1985
8.8
1988 to 1998 2009 to 2015 Post-rehabilitation
0.09
Dissolved Copper Concentrations in EBFR, 2009 to 2015
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60 µg/L (LDWQO)
1500 µg/L (drinking water)
Locally Derived Water Quality Objectives (LDWQOs)
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60 µg/L Cu
28 µg/L Cu
8 µg/L Cu
4 µg/L Cu Not shown: SO4, Al, Co, Fe, Mg, Mn, Ni and Zn
From Hydrobiology (2015)
Test Pitting – WRD and Contaminated Areas
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Preferred Rehabilitation Strategy
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Existing tailings
60% PAF-I
40% PAF-II
18% PAF-II
32% PAF-III
16% Soils
34% NAF
7.1 Mt (New WSF)
4 Mt (Main Pit)
From O’Kane Consultants (2016)
Conceptual Waste Storage Facility (WSF) Design
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Main Pit (backfilled)
From O’Kane Consultants (2016)
3.5 m thick
MODFLOW/MT3D Model Domain and Boundary Conditions
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Simulated Contaminant Plumes (Pre-Rehabilitation), 1984
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Dyson’s WRD
Main WRD
Intermediate WRD
Dyson’s Pit
Former heap leach area
Old Tailings Dam area
Browns Pit
Former plant (ore stockpile)
Sulfate, mg/L
Copper, mg/L
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Simulated Contaminant Plumes (Current Conditions), 2015
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Dyson’s WRD
Main WRD
Intermediate WRD
Dyson’s (backfilled )
Pit
Former heap leach area
Old Tailings Dam area
Browns Pit
Former plant (ore stockpile)
Sulfate, mg/L
Copper, mg/L
Predicted Contaminant Plumes (Post-Rehabilitation), 2045
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Backfilled Pit
New WSF
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Residual Copper Plumes Sulfate, mg/L
0
500
1000
1500
2000
0 10 20 30
SO4 L
oad,
t/ye
ar
Time since rehabilitation, years 0
200
400
600
0 10 20 30
SO4 L
oad,
t/ye
ar
Time since Rehabilitation (yr)
0
200
400
600
0 10 20 30
SO4 L
oad,
t/ye
ar
Time since Rehabilitation (yr)
0
200
400
600
0 10 20 30
SO4 L
oad,
t/ye
ar
Time since rehabilitation, years
0
200
400
600
0 10 20 30
SO4 L
oad,
t/ye
ar
Time since rehabilitation, years
0
200
400
600
0 10 20 30
SO4 L
oad,
t/ye
ar
Time since rehabilitation, years
Total Flux to EBFR (All Reaches)
419 t/year SO4 (-71%)
Predicted Sulfate Loads to EBFR
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Predicted Copper Loads to EBFR
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0.000
0.005
0.010
0.015
0.020
0 5 10 15 20 25 30
Cop
per L
oad
(Flu
x), t
/yea
r
Time since rehabilitation, years
Predicted Copper Concentrations in EBFR
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Before initial rehabilitation in 1984/1985
8.8
Post-rehabilitation (current site configuration)
0.09
0.008 Predicted (30 years post-rehab)
Path Forward
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o DPIR (the ‘Proponent’) intends to submit an EIS to NT EPA by mid-2019 and Detailed Business Case (DBC) by end of 2019
o Refinements being considered (Stage 2A): • Main Pit configuration: (i) covered landform or (ii) flooded above backfill. • New WSF location: (i) northern or (ii) central location). • Post-rehab seepage (SD) management: WTP, MNA, and/or passive options.
o Other issues to be addressed: • Re-vegetation treatments and weed management • Borrow area and haul road disturbances (on Finniss River Land Trust)
o Each refinement/issue has environmental and social implications that require Traditional Owner (TO) input.
o Financial and liability implications for Commonwealth Government of Australia must also be considered in NT’s DBC.
Questions/Comments
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