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SEC Technical Report Summary Pre-Feasibility Study Greenbushes Mine Western Australia
Effective Date: December 31, 2022 Report Date: February 14, 2023 |
Report Prepared for Albemarle Corporation 4350 Congress Street Suite 700 Charlotte, North Carolina 28209 |
Report Prepared by SRK Consulting (U.S.), Inc. 999 Seventeenth Street, Suite 400 Denver, CO 80202
SRK Project Number: USPR000574 |
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Table of Contents
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List of Tables
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List of Figures
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List of Abbreviations
The metric system has been used throughout this report. Tonnes are metric of 1,000 kg, or 2,204.6 lb. All currency is in U.S. dollars (US$) unless otherwise stated.
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Abbreviation | Unit or Term |
A | ampere |
AA | atomic absorption |
A/m2 | amperes per square meter |
ANFO | ammonium nitrate fuel oil |
Ag | silver |
Au | gold |
AuEq | gold equivalent grade |
°C | degrees Centigrade |
CCD | counter-current decantation |
CIF | cost-insurance-freight |
CIL | carbon-in-leach |
CoG | cut-off grade |
cm | centimeter |
cm2 | square centimeter |
cm3 | cubic centimeter |
cfm | cubic feet per minute |
ConfC | confidence code |
CRec | core recovery |
CSS | closed-side setting |
CTW | calculated true width |
° | degree (degrees) |
dia. | diameter |
EIS | Environmental Impact Statement |
EMP | Environmental Management Plan |
FA | fire assay |
FOS | fine ore stockpile |
FoS | factor of safety |
ft | foot (feet) |
ft2 | square foot (feet) |
ft3 | cubic foot (feet) |
g | gram |
gal | gallon |
g/L | gram per liter |
g-mol | gram-mole |
gpm | gallons per minute |
g/t | grams per tonne |
ha | hectares |
HDPE | Height Density Polyethylene |
hp | horsepower |
HTW | horizontal true width |
ICP | induced couple plasma |
ID2 | inverse-distance squared |
ID3 | inverse-distance cubed |
IFC | International Finance Corporation |
ILS | Intermediate Leach Solution |
kA | kiloamperes |
kg | kilograms |
km | kilometer |
km2 | square kilometer |
koz | thousand troy ounce |
kt | thousand tonnes |
kt/d | thousand tonnes per day |
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kt/y | thousand tonnes per year |
kV | kilovolt |
kW | kilowatt |
kWh | kilowatt-hour |
kWh/t | kilowatt-hour per metric tonne |
L | liter |
LCE | Lithium Carbonate Equivalent |
L/s | liters per second |
L/s/m | liters per second per meter |
lb | pound |
LHD | Long-Haul Dump truck |
LLDDP | Linear Low Density Polyethylene Plastic |
LOI | Loss On Ignition |
LoM | Life-of-Mine |
m | meter |
m2 | square meter |
m3 | cubic meter |
masl | meters above sea level |
MARN | Ministry of the Environment and Natural Resources |
mg/L | milligrams/liter |
mm | millimeter |
mm2 | square millimeter |
mm3 | cubic millimeter |
MME | Mine & Mill Engineering |
Moz | million troy ounces |
Mt | million tonnes |
MTW | measured true width |
MW | million watts |
m.y. | million years |
NGO | non-governmental organization |
NI 43-101 | Canadian National Instrument 43-101 |
OSC | Ontario Securities Commission |
oz | troy ounce |
% | percent |
PLC | Programmable Logic Controller |
PLS | Pregnant Leach Solution |
PMF | probable maximum flood |
ppb | parts per billion |
ppm | parts per million |
QA/QC | Quality Assurance/Quality Control |
RC | rotary circulation drilling |
RoM | Run-of-Mine |
RQD | Rock Quality Description |
SEC | U.S. Securities & Exchange Commission |
sec | second |
SG | specific gravity |
SPT | standard penetration testing |
st | short ton (2,000 pounds) |
t | tonne (metric ton) (2,204.6 pounds) |
t/h | tonnes per hour |
t/d | tonnes per day |
t/y | tonnes per year |
TSF | tailings storage facility |
TSP | total suspended particulates |
µm | micron or microns |
V | volts |
VFD | variable frequency drive |
W | watt |
XRD | x-ray diffraction |
y | year |
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SEC Technical Report Summary – Greenbushes Mine | Page 1 |
1Executive Summary
This report was prepared as a Prefeasibility-level Technical Report Summary in accordance with the Securities and Exchange Commission (SEC) S-K regulations (Title 17, Part 229, Items 601 and 1300 until 1305) for Albemarle Corporation (Albemarle) by SRK Consulting (U.S.), Inc. (SRK) on the Greenbushes Mine (Greenbushes). This report is an update of the previous report titled "SEC Technical Report Summary, Pre-Feasibility Study, Greenbushes Mine Western Australia. Amended Date December 16, 2022”.
Greenbushes is held within the operating entity, Talison Lithium Australia Pty Ltd (Talison), of which Albemarle is a 49% owner with the remaining 51% ownership controlled by a Joint Venture (Tianqi/IGO JV) between Tianqi Lithium (Tianqi) and IGO Ltd (IGO) with ownership of 26.01% and 24.99%respectively.
SRK’s reserve estimate is based on the production of chemical grade spodumene concentrate from three existing processing facilities, the two existing chemical grade plants (CGP1 and CGP2) as well as the existing technical grade (TGP) spodumene plant, and the expansion chemical grade plants (CGP3 and CGP4). Talison’s future production from the technical grade plant is planned to target technical grade spodumene products. However, classification of resource applicable for processing as technical grade product does not occur until the grade-control drilling stage and therefore adequate data is not available to characterize production from this plant as technical grade for this reserve estimate. Instead, production from this plant has been assumed as lower value (on average) chemical grade product.
Talison is operating a processing facility to recover lithium from historic tailings (tailings retreatment plant or TRP). SRK has excluded the TRP from its reserve estimate due to limited materiality and technical data underlying the resource.
1.1Property Description (Including Mineral Rights) and Ownership
The Greenbushes property is a large mining operation located in Western Australia extracting lithium and tantalum products from a pegmatite orebody. In addition to being the longest continuously operated mine in Western Australia, the Greenbushes pegmatite is one of the largest known spodumene pegmatite resources in the world. The Greenbushes Lithium Operations property area is approximately 2,000 ha, which is a smaller subset of a larger 10,067 ha land package controlled by Talison. Talison holds 100% of 10,067 ha of mineral tenements which cover the Greenbushes Lithium Operations area and surrounding exploration areas.
1.2Geology and Mineralization
The Greenbushes pegmatite deposit consists of a primary pegmatite intrusion (Central Lode) with a smaller, sub-parallel pegmatite to the east (Kapanga). The primary intrusion and its subsidiary dikes and pods are concentrated within shear zones within a metamorphic belt consisting of granofels, ultramafic schists and amphibolites. The pegmatites are crosscut by mafic dolerite dikes. The Central Lode pegmatite is over 3 kilometers (km) long (north by northwest), up to 300 meters (m) wide (normal to dip), strikes north to north-west and dips moderately to steeply west to south-west. The Kapanga deposit sits approximately 300 m to the east of the Central Lode deposit with strike length
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of 1.8 km, thickness averaging 150 m and dips between 40° and 60° toward the west. Current drilling has defined the Kapanga deposit to approximately 450 m depth below surface.
Overall, the Greenbushes pegmatite averages approximately 2% Li2O. Major minerals are quartz, spodumene, albite, and K-feldspar. Primary lithium-bearing minerals are spodumene, LiAlSi2O6 (approximately 8% Li2O) and spodumene varieties kunzite and hiddenite. Minor lithium minerals include lepidolite (mica), amblygonite and lithiophilite (phosphates).
1.3Status of Exploration, Development and Operations
SRK notes that the property is an active mining operation with a long history of tin, tantalum, and lithium mining. The results and interpretation from exploration data is supported by extensive drilling and active mining exposure of the orebody in multiple pits on the property. The area around the current Greenbushes Lithium Operations has been extensively mapped, sampled, and drilled over several decades of exploration work. For the purposes of this report, the active mining, drilling, and in-pit mapping are considered robust for exploration work to support the current mineral resource estimation.
1.4Mineral Resource and Mineral Reserve Estimates
1.4.1Mineral Resources
The Mineral Resource disclosed are based on a property-wide resource block model comprised of the 2020 Central Lode and the 2020 Kapanga deposit models combined during 2021. Changes from the previous resource statement include the inclusion of Kapanga mineral resources, depletion of the Central Lode model due to mining activities during the calendar year 2022, and revised pit optimization and cut-off grade (CoG) parameters. The mineral resource statement disclosed in this TRS has an effective date of December 31, 2022. These reflect adjustments in property topography, economics, or other factors which have not modified the underlying data such as drilling, geology models, or block models.
Mineral resources have been estimated by SRK and are based on a spodumene concentrate sales price of US$1,650 CIF China, which is US$1,523/t of concentrate at the mine gate after deducting for transportation and government royalty. The applied resource CoG used reflects current operational practices at 0.7% Li2O. All resources are categorized in a manner consistent with SEC definitions. Mineral resources have been reported using an optimized pit shape, based on economic and mining assumptions to support the reasonable prospects for economic extraction of the resource. Current mineral resources, exclusive of reserves, are summarized in Table 1-1.
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Table 1-1: Greenbushes Summary Mineral Resources Exclusive of Mineral Reserves as of December 31, 2022- Based on US$1,523/t of Concentrate at Mine Gate– SRK Consulting (U.S.), Inc.
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Area | Category | 100% Tonnes (Mt) | Attributable Tonnes (Mt) | Li2O (%) | Cut-Off (% Li2O) | Mass Yield | 100% Concentrate Tonnes at 6.0% Li2O (Mt) | Attributable Concentrate Tonnes at 6% Li2O (Mt) | 100% Li Metal in Concentrate (Kt) | Attributable Li Metal in Concentrate (Kt) |
Resource Pit 2022 | Indicated | 44.4 | 21.8 | 1.53 | 0.7 | 16.4 | 7.3 | 3.6 | 203.0 | 99.5 |
Inferred | 57.7 | 28.3 | 1.15 | 0.7 | 11.3 | 6.5 | 3.2 | 181.1 | 88.7 |
Source: SRK, 2023
•Albemarle’s attributable portion of mineral resources is 49%.
•Mineral resources are reported exclusive of mineral reserves. Mineral resources are not mineral reserves and do not have demonstrated economic viability.
•Resources have been reported as in situ (hard rock within an optimized pit shell).
•Resources have been categorized subject to the opinion of a QP based on the quality of informing data for the estimate, consistency of geological/grade distribution, data quality, and have been validated against long term mine reconciliation.
•Resources which are contained within the mineral reserve pit design may be excluded from reserves due to an Inferred classification.
•All stockpiled resources have been converted to mineral reserves.
•Mineral resources tonnage and contained metal have been rounded to reflect the accuracy of the estimate, and numbers may not add due to rounding.
oThe mass yield for resources processed through the chemical grade plants is estimated based on Greenbushes’ mass yield formula, which is Yield%=9.362*(Li2O %)^1.319, subject to a 97% recovery limitation when the Li2O grade exceeds 5.5%.
oDerivation of economic CoG for resources is based on the mine gate pricing of US$1,523/t of 6% Li2O concentrate. The mine gate price is based on US$1,650/t-conc CIF less US$127/t-conc for government royalty and transportation to China.
oCosts estimated in Australian Dollars were converted to U.S. dollars based on an exchange rate of 1.00AU$:0.72US$.
oThe economic CoG calculation is based on US$2.79/t-ore incremental ore mining cost, US$23.35/t-ore processing cost, US$3.57/t-ore G&A cost, and US$1.88/t-ore sustaining capital cost. Incremental ore mining costs are the costs associated with the RoM loader, stockpile rehandling, grade control assays and rockbreaker.
oThe price, cost and mass yield parameters produce a calculated resource economic CoG of 0.319% Li2O. However, due to the internal constraints of the current operations, an elevated resource CoG of 0.7% Li2O has been applied. SRK notes actual economic CoG is lower, but it is the QP’s opinion to use a 0.7% Li2O CoG to align with current site practices.
oAn overall 42° (east side) and 46° (west side) pit slope angle, 0% mining dilution, and 100% mining recovery.
oResources were reported above the assigned 0.7% Li2O CoG and are constrained by an optimized 0.95 revenue factor pit shell.
oNo infrastructure movement capital costs have been added to the optimization.
•Mineral resources tonnage and contained metal have been rounded to reflect the accuracy of the estimate, and numbers may not add due to rounding.
•SRK Consulting (U.S.) Inc. is responsible for the mineral resources with an effective date: December 31, 2022.
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1.4.2 Mineral Reserve Estimate
The conversion of mineral resources to mineral reserves has been completed in accordance with United States Security and Exchange Commission (SEC) regulations CFR 17, Part 229 (S-K 1300). Mineral reserves were determined based on a spodumene concentrate sales price of US$1,500/t of concentrate CIF China (or US$1,381/t of concentrate at the mine gate after deducting for transportation and government royalty). The mineral reserves are based on PFS level study as defined in §229.1300 et seq.
The mineral reserve calculations for the Greenbushes Central Lode lithium deposit have been carried out by a Qualified Person as defined in §229.1300 et seq. SRK Consulting (U.S.) Inc. is responsible for the mineral reserves reported herein. Table 1-2 shows the Greenbushes mineral reserves with an effective date of December 31, 2022.
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Table 1-2: Greenbushes Summary Mineral Reserves at December 31, 2022 Based on US$1,381/t of Concentrate Mine Gate – SRK Consulting (U.S.), Inc.
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Classification | Type | 100% Tonnes (Mt) | Attributable Tonnes (Mt) | Li2O% | Mass Yield (%) | 100% Concentrate (Mt) | Attributable Concentrate (Mt) | 100% Li Metal in Concentrate (Kt) | Attributable Li Metal in Concentrate (Kt) |
Probable Mineral Reserves | In situ | 153.1 | 75.0 | 1.91 | 22.2 | 34.0 | 16.7 | 947.8 | 464.4 |
Stockpiles | 4.0 | 2.0 | 1.99 | 22.2 | 0.9 | 0.4 | 24.4 | 11.9 |
In situ + Stockpiles | 157.1 | 77.0 | 1.91 | 22.2 | 34.9 | 17.1 | 972.2 | 476.4 |
Source: SRK, 2022
Notes to Accompany Mineral Reserve Table:
•Albemarle’s attributable portion of mineral resources and reserves is 49%.
•Mineral reserves are reported exclusive of mineral resources.
•Indicated in situ resources have been converted to Probable reserves.
•Measured and Indicated stockpile resources have been converted to Probable mineral reserves.
•Mineral reserves are reported considering a nominal set of assumptions for reporting purposes:
oMineral reserves are based on a mine gate price of US$1,381/t of chemical grade concentrate (6% Li2O).
oMineral reserves assume 93% global mining recovery.
oMineral reserves are diluted at approximately 5% at zero grade for all mineral reserve blocks in addition to internal dilution built into the resource model (2.7% with the assumed selective mining unit of 5 m x 5 m x 5 m).
oThe MY for reserves processed through the chemical grade plants is estimated based on Greenbushes’ mass yield formula, which is Yield%=9.362*(Li2O %)^1.319, subject to a 97% recovery limitation when the Li2O grade exceeds 5.5%. The average LoM mass yield for the chemical grade plants is 22.2%.
oThe MY for reserves processed through the technical grade plant is estimated based on Greenbushes’ mass yield formula, which is Yield%=(31.792* Li2O %)–80.809. There is approximately 3.2 Mt of technical grade plant feed at 3.7% Li2O. The average LoM mass yield for the technical grade plant is 37.5%.
oAlthough Greenbushes produces a technical grade product from the current operation, it is assumed that the reserves reported herein will be sold as a chemical grade product. This assumption is necessary because feed for the technical grade plant is currently only defined at the grade control or blasting level. Therefore, it is conservatively assumed that concentrate produced by the technical grade plant will be sold at the chemical grade product price
oDerivation of economic CoG for reserves is based on mine gate pricing of US$1,381/t of 6% Li2O concentrate. The mine gate price is based on US$1,500/t-conc CIF less US$119/t-conc for government royalty and transportation to China.
oCosts estimated in Australian Dollars were converted to U.S. dollars based on an exchange rate of 1.00AU$:0.72US$.
oThe economic CoG calculation is based on US$2.79/t-ore incremental ore mining cost, US$23.35/t-ore processing cost, US$3.57/t-ore G&A cost, and US$1.88/t-ore sustaining capital cost. Incremental ore mining costs are the costs associated with the RoM loader, stockpile rehandling, grade control assays and rockbreaker.
oThe price, cost and mass yield parameters produce a calculated economic CoG of 0.344% Li2O. However, due to the internal constraints of the current operations, an elevated mineral reserves CoG of 0.7% Li2O has been applied.
oThe CoG of 0.7% Li2O was applied to reserves that are constrained by the ultimate pit design and are detailed in a yearly mine schedule.
oStockpile reserves have been previously mined and are reported at a 0.7% Li2O CoG.
•Waste tonnage within the reserve pit is 701.5 Mt at a strip ratio of 4.58:1 (waste to ore – not including reserve stockpiles)
•Mineral reserve tonnage, grade and mass yield have been rounded to reflect the accuracy of the estimate, and numbers may not add due to rounding:
oMt = millions of metric tonnes
oReserve tonnes are rounded to the nearest hundred thousand tonnes
•SRK Consulting (U.S.) Inc. is responsible for the mineral reserves with an effective date: December 31, 2022.
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1.5Mining Operations
Greenbushes is an operating mine using conventional open pit mining methods to extract mineral reserves containing economic quantifies of Li2O to produce both chemical and technical grade spodumene concentrates. Drilling, blasting, and load and haul activities are performed by contractors. Grade control is performed with reverse circulation (RC) drills that sample on 2.5 m intervals. In ore areas, mining occurs on 5 m benches and in waste areas, 10 m benches are used. Ore is hauled to the run-of-mine (RoM) pad or to long-term ore stockpiles. Waste rock is hauled to a waste dump adjacent to the open pit.
The pit design has been checked for geotechnical stability. Rock mass parameters based on characterization work have been input according to structural domain into a limit equilibrium stability analysis. Results of the stability analyses indicate that all slopes meet the minimum acceptability criteria of factor of safety greater than 1.3.
The life-of-mine (LoM) production profile is shown in Figure 1-1. The peak annual material movement is approximately 56 Mt and mining spans approximately 19 years. The LoM average strip ratio (w:o) is 5.48.
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Source: SRK, 2023
Figure 1-1: Mine Production Profile
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1.6Mineral Processing and Metallurgical Testing
SRK notes that Greenbushes Chemical Grade Plant -1 (CGP1) is a mature operation and was used as basis for design of Greenbushes new Chemical Grade Plant-2 (CGP2) CGP2 processes ore from the same orebody using essentially the same flowsheet as CGP1. As a result, incorporation of process improvements at CGP2 is based on opportunities identified by Greenbushes during operation of CGP1, rather than on new fundamental metallurgical testing. SRK is of the opinion that this is an adequate basis for CGP2 design given that the CGP2 process flowsheet is based on the CGP1 flowsheet and that CGP2 would process ore from the same orebody as CGP1. SRK notes that Greenbushes did conduct metallurgical testwork to support a change to the comminution circuit that incorporates high pressure grinding rolls (HPGR) in CGP2, instead of the ball mill grinding circuit used in CGP1. This work resulted in the development of a yield model that estimates incrementally higher lithium recovery in CGP2, which is attributed to HPGR comminution instead of ball mill grinding as practiced in CGP1. This additional lithium recovery has not yet been demonstrated during CGP2 commissioning and initial operations.
1.7Processing and Recovery Methods
Greenbushes currently has two ore crushing facilities (CR1 and CR2) and three ore processing plants which include a technical grade plant (TGP), chemical grade plant-1 (CGP1) and chemical grade plant-2 (CGP2) with a nominal capacity of 4.5 Mt/y of pegmatite feed to produce a nominal 1.3 Mt/y of spodumene concentrate from all three plants combined. TGP is a relatively small plant that processes approximately 350,000 t/y of ore at an average grade of about 3.8% Li2O and produces about 150,000 t of spodumene concentrate products. TGP produces a variety of product grades identified as SC7.2, SC6.8, SC5.5 and SC5.0.
During 2022 TGP processed (Table 14-2) 370,893 t of ore at an average grade of 3.94% Li2O and recovered 72.5% of the contained lithium into six separate products (SC7.2-Standard, SC7.2-Premium, SC6.8, SC6.5, SC6.0 and SC5.0).
CGP1 and CGP2 process spodumene ore into lithium concentrates containing a minimum of 6% Li2O and a maximum iron content of 1% iron oxide (Fe2O3). The process flowsheets utilized by both CGP1 and CGP2 are similar and include the following major unit operations to produce chemical grade spodumene concentrates:
•Crushing
•Grinding and classification
•Heavy media separation
•Wet high intensity magnetic separation (WHIMS)
•Coarse mineral flotation
•Regrinding
•Regrind coarse mineral flotation
•Fine mineral flotation
•Concentrate filtration
•Final tailings thickening and storage at the tailing storage facility
During 2022 CGP1 processed 1.79 Mt of ore at an average grade of 2.69% Li2O and recovered 72.1% of the contained lithium into concentrates averaging 6.06% Li2O, representing a mass yield of 32%.
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CGP2 commissioning began during September 2019 and continued through April 2020 and was then shut down and put on care and maintenance during the period from March 2020 to April 2021 due to market demand considerations. CGP2 was then put back into production during May 2021.
During 2021 (May to December), CGP2 processed 1,387,985 t of ore at an average grade of 1.97% Li2O and recovered 50.5% of the lithium (versus a predicted recovery of 73%) into 229,521 t of concentrate at an average grade of 5.88% Li2O. Concentrate yield for this period averaged 16.5% versus the model yield projection of 24.5%. Although, product quality specifications were generally achieved, lithium recovery and concentrate yield were substantially below target.
During 2022 CGP2 processed 1,999,006 t of ore at an average grade of 1.96% Li2O and recovered 64.0% of the lithium (versus a predicted recovery of 74.3%) into 419,246 t of concentrate at an average grade of 5.98% Li2O. CGP2 performance improved steadily during 2022 with significant improvement during the fourth quarter. During the fourth quarter of 2022 lithium recovery averaged 68.2% versus a predicted recovery of 75.4%. The improved plant performance is attributed to improved operating availability, steady-state operation and ongoing efforts to improve performance of individual unit operations. As part of this effort, Greenbushes retained MinSol Engineering to undertake a performance assessment of CGP2 and identify areas where improvements in the plant could be made to increase lithium recovery. MinSol identified and coordinated process plant improvements which resulted in increasing lithium recovery from about 50% reported for 2021 to the Q4 2022 average of 68%. This represents an 18% increase in recovery.
Lithium recovery remains about 8% less than the design recovery and MinSol has identified additional process improvements for CGP2 that could be implemented during 2023 in an effort to achieve the original design lithium recovery.
SRK notes that that CGP2 and CGP1 flowsheets are similar and both plants process ore from the same mining operation, as such, SRK believes that it is reasonable to expect that CGP2 will eventually achieve performance similar to CGP1. SRK is of the opinion that the incrementally higher lithium recovery included in Greenbushes CGP2 yield model (attributed to the inclusion of the HPGR in CGP2’s comminution circuit) is not warranted as it has been determined that the HPGR results in higher unrecoverable lithium slimes production than had been anticipated. SRK recommends that Greenbushes CGP1 yield model be used for both for CGP1 and CGP2 for resource and reserve modeling to provide estimates of mass yield and lithium recovery at various ore grades in the mine plan.
Greenbushes is currently constructing Chemical Grade Plant-3 (CGP3), which will be identical to CGP2 with a capacity of 2.4 Mt/y. CGP3 is scheduled to come on-line during Q2 2025. Greenbushes also has plans to construct Chemical Grade Plant-4 (CGP4), which will also be based CGP2. CGP4 is currently planned to commence production during Q1 2027. For purposes of resource and reserve mine planning SRK recommends that Greenbushes’ yield model for CGP1 be used to estimate future production from CGP3 and CGP4.
1.8Infrastructure
Greenbushes is a mature operating lithium hard rock open pit mining and concentration project that produces lithium carbonate. Access to the site is by paved highway off of a major Western Australian highway. Employees travel to the project from various communities in the region. The established facilities on the site include security fencing and guard house access, communications systems,
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access roads and interior site roads, administrative and other offices, change houses, existing mine services area (MSA), warehousing, shops, crushing plants, processing plants (CGP1/CGP2/TGP/TRP), tailings facilities, new explosives storage facilities, water supply and distribution system with associated storage dams, power supply and distribution system, laboratory, fuel storage and delivery system, reverse-osmosis water treatment plant, health-safety-training offices, mine rescue area, storage sheds, mine waste storage area, miscellaneous waste storage facilities, and engineering offices. The concentrate is shipped by truck to port facilities located at Bunbury 90 km to the east of the Project. These facilities are in place and functional. An abandoned rail line is present north of the project but not currently used.
Several modifications to the infrastructure are currently in construction or planned. An upgraded 132 kV power line will be placed in service by 2023. A new Mine Service Area (MSA) will be constructed and operating in mid-2023 to provide mine heavy and light equipment maintenance facilities and technical services offices as the existing MSA will be impacted by the planned pit progression. A mine access road will be added to reduce truck traffic through Greenbushes. The warehouse and laboratories are planned to be expanded. The tailings facilities are being expanded with the addition of a new two cell facility known as TSF4 located adjacent to and south of the existing TSF2 and TSF1 facilities. TSF1 will be expanded late in the mine life to meet tailings storage needs. The waste rock facilities will continue to expand on the west side of the pit toward the highway and south toward the permit boundary adjacent to TSF4. A new mine village will be constructed starting in 2023 to provide additional housing. It is expected to be completed in Q1 2024.
1.9Environmental Studies, Permitting, and Plans, Negotiations, or Agreements with Local Individuals or Groups
The Project has been in operation as a hard rock mine since 1983 and is fully permitted for its current operations. The Project is in the process of obtaining further approvals for expansion; however, consideration of the expansion has been excluded from this evaluation, as detailed assessment information is not yet available. Talison holds the mining rights to lithium at the Project and Global Advanced Metals (GAM) holds the rights to non-lithium minerals. GAM processes tantalum and tin extracted by Talison during mining activities within the Project area under their own operating license and GAM are, therefore, responsible for the environmental management of their premises. Under agreement, Talison provides services to GAM consisting of laboratory analyses and environmental reporting, and shared use of some water circuit infrastructure.
Environmental Study Results
The Project is in the southwest of Western Australia in the Shire of Bridgetown-Greenbushes. The town of Greenbushes is located on the northern boundary of the mine. The majority of the Project is within the Greenbushes Class A State Forest (State Forest 20) which covers 6,088 ha and is managed by the Department of Biodiversity, Conservation and Attractions (DBCA) as public reserve land under the Conservation and Land Management Act 1984 (CALM Act). The DBCA manages State Forest 20 in accordance with the Forest Management Plan 2014-2023, that aims to maintain the overall area of native forest and plantation available for forest produce, including biodiversity and ecological integrity. The remaining land in the Project area is privately owned.
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During development and subsequent modifications to the mine, environmental studies and impact assessments have been completed to support project approval applications, including studies related to:
•Flora and vegetation
•Terrestrial and aquatic fauna
•Surface water and groundwater
•Material characterization (geochemistry)
•Air quality and greenhouse gas assessment
•Noise, vibration and visual amenity
•Cultural Heritage
Environmental Management and Monitoring
The Project operates under approvals that contain conditions for environmental management that include waste and tailings disposal, site monitoring, and water management. Primary approvals are authorized under the federal Environment Protection and Biodiversity and Conservation Act of 1999 (EPBC Act), the Environmental Protection Act of 1986 (EP Act) including the environmental impact assessment approval for the proposed mine expansion (Ministerial Statement 1111), the operation of a prescribed premises (License L4247/1991/13), approval for the construction and commissioning of a prescribed premises for the proposed mine expansion (W6283/2019/1), and under the Mining Act of 1978, under an approved Mine Closure Plan (Reg ID 60857) and several Mining Proposals (section 17.3) conditions.
Specific requirements for compliance and ambient monitoring are defined in the License (L4247/1991/13) and Works Approval (W6283/2019/1). The monitoring results must be reported to the regulators (DWER and DMIRS) on an annual basis and include point source emissions to surface water, including discharge and seepage locations, process water monitoring, permitted emission points for waste discharge to surface water, ambient surface water quality and ambient groundwater quality monitoring, ambient surface water flow and each spring, complete an ecological assessment of four sites upstream and six sites downstream of the Norilup Dam.
Project Permitting Requirements
Australia has a robust and well-developed legislative framework for the management of the environmental impacts from mining activities. Primary environmental approvals are governed by the federal EPBC Act and the environmental impact assessment process in Western Australia is administered under Part IV of the EP Act. Additional approvals in Western Australia are principally governed by Part V of the EP Act and by the Mining Act, as well as several other regulatory instruments. Primary and other key approvals are discussed in Section 17.
Environmental Compliance
The Project has not incurred any significant environmental incidents (EPA, 2020). Through the end of 2022 there were 14 non-conformance events reported to regulators.
The Project is responsible for contamination of five sites due to hydrocarbons and metals in soil, and elevated concentrations of metals in groundwater and surface water (Site IDs 34013, 73571, 73572, 75019, and 75017). These sites are classified as “Contaminated – Restricted use” and only permit commercial and industrial uses. This will need to be reviewed for final land use options for closure.
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Local Individuals and Groups
The mining tenure for the Project was granted in 1983 and, therefore, is not a future act as defined under the Native Title Act of 1993 (a 'future act' is an act done after the January 1, 1994, which affects Native Title). The Project is, therefore, not required to have obtained agreements with the local native title claimant groups.
The Project lies immediately south of the town of Greenbushes and maintains an active stakeholder engagement program and information sessions to groups such as the “Grow Greenbushes.” Senior mine management reside in the town. Talison promotes local education (the Greenbushes Primary School and tertiary sponsorships) and provides support community groups with money and services (allocated in the Environmental and Community budget).
Talison has two agreements in place with local groups:
•Blackwood Basin Group (BBG) Incorporated – offset management agreement whereby BBG have agreed to manage and improve the condition of native vegetation for the purpose of the Black Cockatoo offset requirements.
•Tonebridge Grazing Pty Ltd. – site conservation agreement for the protection and improvement of native vegetation to protect Black Cockatoo habitat.
Mine Closure
Talison has a mine closure plan submitted and approved by DMIRS on 23 February 2017, with their costs updated in October 2016.
Western Australia does not require a company to post performance or reclamation bonds. All tenement holders in Western Australia are required to annually report disturbance and to make contributions to a pooled fund based on the type and extent of disturbance under the Mining Rehabilitation Fund Act of 2012 (MRF Act). The pooled fund can be used by the Department of Mines, Industry Regulation and Safety (DMIRS) to rehabilitate mines where the tenement holder/operator has failed to meet their rehabilitation obligations and finances have not been able to be recovered. The interest earned on the pooled fund is used for administration and to rehabilitate legacy abandoned mine sites.
A cost estimate for immediate (unplanned) closure of Greenbushes has been prepared by Talison using the Victorian Government Rehabilitation bond calculator (dpi-bond-calculator-24-feb-2011) as a template to assist them in identifying and costing the rehabilitation, decommissioning, and monitoring requirements for the Greenbushes site. The Victorian Government bond calculator uses predefined third-party unit rates based on the typical current market ‘third party rates’ as of July 2010, which may overestimate or underestimate closure costs for Western Australia. Talison has been escalating these unit rates since 2013.
The latest version of the closure cost estimate available for review was the 2020 draft estimate. It only includes the facilities that were on site at that time and does not include any future expansions. Changes to the site during 2020, and any future plans, are not included. This closure cost estimate totals AU$37,232,334 for Talison’s portion of the operation. GAM is responsible for closure for the remainder of the site. SRK understands that an updated model has been submitted to the authorities but as it has not been approved it is not reviewed as part of this report.
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The Victorian Government model used by Talison to estimate closure costs was designed in 2011 using 2010 rates. It does not use site-specific rates as is good industry practice. There is no documentation on the basis of the unit rates used in the Victorian model and the government of Victoria was unable to provide any information regarding the accuracy of the rates. Because of this, SRK cannot validate any of the unit rates used in the model or the overall closure cost estimate.
Furthermore, because closure of the site is not expected until 2056, the closure cost estimate represents future costs based on current site conditions. In all probability, site conditions at closure will be different than currently expected and, therefore, the current estimate of closure costs is unlikely to reflect the actual closure cost that will be incurred in the future.
Currently, the site must treat mine water collecting in the Southampton and Cowan Brook Dams prior to discharge due to elevated levels of arsenic and lithium in the water. The sources of elevated lithium and arsenic in the mine water circuit include dewatering water from the open pit. However, there has been no study to determine if water that will eventually collect in the pit or from any other point source and discharge will meet discharge water quality standards. Therefore, no assessment of the probability that post-closure water management or water treatment has been performed.
Additionally, contaminated seepage from TSF2 has recently been observed in the alluvial aquifer and is now being collected via French drains constructed along the toe of the embankment and conveyed to the water treatment plant. At this time, no studies have been conducted to determine the cause of the current seepage, the likelihood and duration of continued seepage, or the possibility that additional seepage could occur from the other TSF facilities.
If perpetual, or even long-term, treatment of water is required to comply with discharge requirements, the closure cost estimate provided by Talison could be materially deficient.
1.10Summary Capital and Operating Cost Estimates
Capital cost forecasts were developed in Australian dollars. The cost associated with the sustaining capital at the operation are presented in Figure 1-2. The total sustaining capital spend over life of mine is forecast at US$1.29 billion.
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Source: SRK
Figure 1-2: Sustaining Capital Profile (Tabular data in Table 19-12)
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Operating costs were forecast in Australian dollars and are categorized as mining, processing and SG&A costs. Mining costs include the costs to move the ore and waste material to waste dumps, stockpiles or plant feed locations. Processing costs include the costs to process the ore into a concentrate. SG&A costs include the general and administrative costs of running the operation and the selling expenses associated with the concentrate product. A summary of the life of mine average for mining, processing and SG&A costs is presented in Table 1-3.
Table 1-3: Life of Mine Operating Cost Averages
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Category | Unit | Value |
Mining Cost | US$/t mined | 5.33 |
Processing Cost | US$/t processed | 23.69 |
SG&A Cost | US$/t concentrate | 64.70 |
Source: SRK, 2023
These costs are typically broken out into fixed and variable costs. A life of mine summary of the operating cost breakdown is presented in Figure 1-3 and Figure 1-4.
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Source: SRK, 2023
Figure 1-3: Life of Mine Operating Cost Profile (Tabular data in Table 19-12)
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Source: SRK
Figure 1-4: Life of Mine Operating Cost Summary
1.11Economics
Economic analysis, including estimation of capital and operating costs is inherently a forward-looking exercise. These estimates rely upon a range of assumptions and forecasts that are subject to change depending upon macroeconomic conditions, operating strategy and new data collected through future operations and therefore actual economic outcomes often deviate significantly from forecasts.
The Greenbushes operation consists of an open pit mine and several processing facilities fed primarily by the open pit mine. The operation is expected to have a 20 year life.
The economic analysis metrics are prepared on annual after tax basis in US$. The results of the analysis are presented in Table 1-4. The results indicate that, at a CIF China chemical grade concentrate price of US$1,500/t, the operation returns an after-tax NPV at 8% of US$13.2 billion (US$6.5 billion attributable to Albemarle). Note, that because the mine is in operation and is valued on a total project basis with prior costs treated as sunk, IRR and payback period analysis are not relevant metrics.
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Table 1-4: Indicative Economic Results (Albemarle)
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LoM Cash Flow (Unfinanced) | Units | Value |
Total Revenue | US$ million | 25,653 |
Total Opex | US$ million | (5,162) |
Operating Margin | US$ million | 20,490 |
Operating Margin Ratio | % | 80% |
Taxes Paid | US$ million | (5,631) |
Free Cashflow | US$ million | 12,972 |
Before Tax |
Free Cash Flow | US$ million | 18,603 |
NPV at 8% | US$ million | 9,048 |
After Tax |
Free Cash Flow | US$ million | 12,972 |
NPV at 8% | US$ million | 6,455 |
Source: SRK
A summary of the cashflow on