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1
Organic Residuals for Mine Reclamation:
an Overview of Progress in Ontario
Bryan Tisch
Compost Council of Canada, Webinar
November 5, 2014
2
Outline
Overview of mining issues (Mining 101)
Success with papermill biosolids
Green Mines Green Energy Initiative
Moving forward – biochar/carbon in
tailings
3
What are Tailings?
Material rejected from a mill
after most of the recoverable
valuable minerals have been
extracted.
6
Growth Constraints in Mine
Waste Particle size and structure
Compaction
Lack of organic matter Lack of nutrients
Lack of soil microbes
pH
Metals
7
Background
Work with papermill biosolids initiated at several sites in Ontario (Rio Algom, Vale, Goldcorp)
Vale (formerly INCO), Glencore (formerly Falconbridge) and city of Toronto - possibility of using composted garbage as a reclamation material for mines.
Proposed biodiesel plant in Sudbury
8
Pronto Mine – Elliot Lake
•First tailings reclamation in Ontario with papermill biosolids. •Excellent vegetation establishment. •Mining company estimated savings of $2 million •Paper company biosolids disposal cost halved.
12
Policy Linkages
Organic waste suppliers – no
commitment until mines agree to take material
Mines - no commitment
until regulators willing to approve
Regulators – no approval until
impacts investigated
NRCan
13
Green Mines Green Energy (GMGE)
3-year field demonstration study led by NRCan
to examine technical feasibility of using residuals
Goal - To advance mine reclamation through the
beneficial use of organic residuals for the
sustainable establishment of bioenergy crops
Potential to contribute feedstock for a planned 20
million litre/year biodiesel plant in Sudbury
14
Scope of the Initiative
Four main target areas proposed:
Impact of Organic Residuals on Tailings
Quantity and Quality of Biomass
Economic Feasibility
Communication, Public Education and
Technology Transfer
15
Primary Participants
Mining: Glencore, Vale, Goldcorp, Barrick Gold, Highland Valley Copper, Enterprise Cape Breton
Forestry: Domtar, St. Marys Paper, Abitibi
Consolidated Government: Natural Resources Canada,
Agriculture Canada, Ont. Ministry of Food & Rural Affairs, Ont. Ministry of Environment
Academia/Other: Laurentian University/MIRARCO,
GroBark, City of Greater Sudbury, Metro Vancouver, Green Municipal Fund, NSERC, ORF
16
Demonstration Locations
Vale (Copper Cliff) – acidic Cu/Ni
tailings
Glencore (Onaping) – desulphurized
slimes layer overlying acidic Cu/Ni
tailings
Goldcorp (Timmins) – alkaline gold
tailings (As bearing)
Cape Breton (ECBC)
British Columbia (Highand Valley
Copper)
17
Potential Benefits of Residuals
Tailings dust suppression
Growth substrate
Decreased metal mobility
Progressive reclamation
Reduced liability for mine waste
One waste to reclaim another
Carbon credits
Biodiversity
Alternative land use (long term)
Diversion of organics from landfill
25
Biomass – corn/canola
0
2
4
6
8
10
12
14
Vale -
Canola
Xstrata -
Canola
Goldcorp -
Canola
Vale - Corn Xstrata -
Corn
Bio
ma
ss
(T
/ha
dw
)
2008
2009
2010
2011
3.3*
0.7*
2.7*
*Seed Yield Ontario Agr. Avg. (2009) was 2.2 T/ha
30
Rough Economics/Energy
Based on GMGE field results….
Sale of biomass also feasible (consideration for companies not
interested in actually producing biofuel)
Potential profit of $905/ha/yr for canola at Vale. If applied to 60% of
their tailings (1,300 ha)…approx. $1.2 million/yr….just on sale of
feedstock. Could generate up to $4.7 million litres/yr of biodiesel.
Site Crop Yield (kg ha-1)
Profit ($ ha-1)
Vale St. Marys Canola 3,273 (seed) 905
Corn 3,378 (seed) -350
Goldcorp Canola 2,748 (seed) 612
Glencore Canola 706 (seed) -363
Corn 2,469 (seed) -515
31
Groundwater Nickel (Vale)
0
100
200
300
400
500
600
700
Aug. 8
/08
Sept.
10/0
8
Sept.
25/0
8
Oct. 3
0/08
Nov
. 4, 2
008
May
20/
09
July 7
/09
Aug. 1
2/09
June
24/
10
July 1
3/10
Aug. 1
8/10
Sept.
29/1
0
Nov
. 30/
10
June
29/
11
July 2
5/11
Aug. 2
3/11
Sept.
29/1
1
Date
Ni (m
g/L
)
St Marys 1.42 m
St Marys 2.2 m
St Marys 3.05 m
2 per. Mov. Avg. (StMarys 1.42 m)2 per. Mov. Avg. (StMarys 2.2 m)2 per. Mov. Avg. (StMarys 3.05 m)
33
Goldcorp (Delnite) – As & Fe
0
2
4
6
8
10
12
14
Jan-07
Mar
-07
May
-07
Jul-0
7
Sep
-07
Nov
-07
Jan-08
Mar
-08
May
-08
Jul-0
8
Sep
-08
Nov
-08
Jan-09
Mar
-09
May
-09
Jul-0
9
Sep
-09
Nov
-09
Jan-10
Mar
-10
May
-10
Jul-1
0
Sep
-10
Nov
-10
Jan-11
Ars
en
ic (
pp
m)
Goldcorp Control
20 cm Abitibi
Goldcorp/Abitibi Mix
1 Metre Abitibi
Abitibi Control
0
2
4
6
8
10
12
Jan-07
Mar-07
May
-07
Jul-0
7
Sep
-07
Nov
-07
Jan-08
Mar-08
May
-08
Jul-0
8
Sep
-08
Nov
-08
Jan-09
Mar-09
May
-09
Jul-0
9
Sep
-09
Nov
-09
Jan-10
Mar-10
May
-10
Jul-1
0
Sep
-10
Nov
-10
Jan-11
Fe (
pp
m)
Goldcorp Control
20 cm Abitibi
Goldcorp/Abitibi Mix
1 Metre Abitibi
Abitibi Control
35
Metal Accumulation (3 – 5 years)
No trend of increasing
metal levels in the
biosolids cover (from
underlying tailings)
observed.
No trend of metal
accumulation in crops
observed.
41
Other Examples
Glencore Kidd Creek (Timmins)
– black muck cover amended
with mun. biosolids (Toronto)
Kamkotia (Timmins) –
considering mun. biosolids
(Toronto) to help reclaim areas
where tailings removed
More to come…
42
Past and Current Research
Goals • Beneficial reuse of wastes • Diverting organics from landfill • Advancing mine reclamation (productive land use)
GMGE 2006-2012
Consultation • City of Toronto • Vale • Glencore • BHP Billiton • Barrick
Thick (1m) Covers Corn Canola Switchgrass Sunflower Willow
Feasibility Study • Currently not economically feasible
Thin covers Canola Switchgrass Willow Sunflower Big Bluestem
BIOCHAR
Glencore 5 ha covered • 10 ha in 2 years • 96 ha total
Compost + Mun. biosolids (GroBark/N-Viro)
Vale ~3 ha Municipal biosolids
(Toronto)
Impact of C-rich amendments on mine
stability 2013-2016
Characterization Feedstock Temperature Residence time
Impact of Covers Geochemical Microbes
Potential Uses • Soil amendment • Metal sorption • Reprocess tailings • Alternative binders
Signature project
43
Science Policy Objectives:
Advance mine reclamation by reuse of organic wastes
Establish long term agri-energy land use on tailings
Improve reclamation options for tailings (i.e. contribute to
social license)
Provide scientific data that documents characteristics of
novel by-products (e.g. biochar)
How can it be used in the mining industry?
Can it be altered to improve metal adsorption?
Improve marketability of products for mining
Potential carbon storage in tailings
44
Biofuel Production
Pyrolysis
Dry
Biomass
Gas
Bio-oil
Char
(20 – 35%)
250ºC
350ºC
600ºC
• Depolyme-
rization
• Am. C
• Polyaromatic
sheets of
graphene
grow
100 µm
45
Impact of C-rich amendments on the long-term stability of mine wastes (2013-2016)
Biochar
Characterization Potential uses
Soil amendment
Metal sorbent
Reprocess tails
Impact of Covers
Post-evaluation GMGE
46
Team: 8 CMIN scientists + …
Collaborators
Ag Canada
Purdue U
Ph. D. student
McGill U
Ph. D. student
Others:
NRC, EC, CanmetENERGY
Industry Stakeholders
Abri-Tech Inc.
Airex Inc.
Pyrovac
Basques
Vale Inc.
47
Soil amendment
As a source for stable C and
nutrient carrier
Next phase for CMIN: scaling up to
experiments in growth chamber
Purdue received $260K grant for
investigating the reclamation of coal
spoils in Indiana (USA)
Metal sorbents
Testing ways to make biochar more
effective metal sorbents (e.g. H2O2
treatment)
Willow and poultry manure derived
biochars were effective sink for Pb
precipitation as pyromorphite =>
potential application currently being
tested for polluted rice lands in
Indonesia
Lab
m-scale
Field
Biochar – Potential uses (on-going)
0
50
100
150
200
250
300
350
0 100 200 300
Cu
se
qu
es
tere
d (
mm
ol
kg
-1)
Cu conc. in solution (mg L-1)
pH 4.5
H2O2-treated
Original
48
Biochar – Characterization 9. Indices for biochar carbon stability
† BW = Basswood; SG = Switchgrass; PM = Poultry manure
Airex 1
BW† 450
BW† 400
Willow 500Willow 450
Airex 2
SG† 500
Basques fineBasques coarse
PM† 500
PM† 450Pyrovac
SG† 450
0.20
0.30
0.40
0.50
0.60
0.70
0.80
0.90
1.00
0.40 0.45 0.50 0.55 0.60 0.65 0.70
Mo
lar
H:O
C
R50
increase in thermal stability
incre
ase
in C
aro
ma
ticity
more stable in soils?
Using a range of biochars derived from various feedstocks and pyrolysis conditions, we
characterized their physico-chemical properties to select the most promising amendments
for reclamation of acidic tailings.
…”a much needed study for all of us manufacturers”…
49
Impact of cover: Post-evaluation GMGE
Results indicate improvement
of “soil health” in the
oxidized, acidic tailings:
increased pH, reduced
metal mobility,
increased microbial
activity and diversity of
populations
The study provides proof-of-
concept to support new
research in BMP for mine
reclamation at national scale
(Genomic proposal; B. Tisch)
Cum
ul µ
g C
O2-C
/g tails
(±
SE)
Microbial activity and diversity in oxidized tailings
(0-5 cm) biosolids
0
20
40
60
80
0 20 40 60 80
Incubation time (day)
Under cover; pH = 4.1
Control; pH = 2.6
Activity
(12 ºC; 30 wt.% Hº)
Diversity
(DGGE: 16s rRNA; ~178 bp)
Ctrl Under cover
0 – 5 cm
Biosolids,
cropped
Control
6 year old field plots, Vale tailings, Sudbury:
Sampled June 2013
(149 m x 21 m)
Paper mill
biosolids
Oxidized tailings
50
General Conclusions
The GMGE initiative has demonstrated the technical feasibility of establishing biofuel crops on tailings while diverting organic residuals form landfill.
Tailings can be converted from strictly a liability
to a profit generating operation that involves local communities.
Availability of sufficient volumes of organic
residuals and cost of establishing the growth medium (cover) remain obstacles to larger scale usage
51
Potential Uses • Soil amendment • Metal sorption • Reprocess tailings • Alternative binders
Next Steps
Goals • Beneficial reuse of wastes • Diverting organics from landfill • Advancing mine reclamation (productive land use)
GMGE
Consultation • City of Toronto • Vale • Glencore • BHP Billiton • Barrick
Thick (1m) Covers Corn Canola Switchgrass Sunflower Willow
Feasibility Study • Currently not economically feasible
Thin covers Canola Switchgrass Willow Sunflower Big Bluestem
BIOCHAR
Characterization Feedstock Temperature Residence time
Impact of Covers Geochemical Microbes
Glencore 5 ha covered • 10 ha in 2 years • 96 ha total Compost + Mun. biosolids
(GroBark/N-Viro)
Vale ~3 ha Municipal biosolids
(Toronto)
Carbon in Tailings • CFS • IETS • Universities • NRC • Mining Industry • Biochar producers
Quantify/Augment C storage in tailings
Soil development
52
Considerations for Moving Forward
Odor control when applying
Collection/consolidation of organic residuals
Manufactured soils
Pharmaceuticals/organic content of
residuals
Interaction with tailings
Sound science and demonstrations
Work with regulators in these projects