5E Advanced Materials, Inc.
For the period ended Jun 30, 2025. Filed Sep 29, 2025.
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FY2025 · Filed Sep 29, 2025
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Item 2. Properties
Properties
Fort Cady Project (AKA 5E Boron Americas Project)
The Project is located in the Mojave Desert region in the high desert in eastern San Bernardino County, California, approximately 36 miles east of Barstow, near the town of Newberry Springs and two miles south of I-40. The Project lies approximately 118 miles northeast of Los Angeles, California, or approximately half-way between Los Angeles and Las Vegas, Nevada. Access to the Project is eastbound from Barstow on I-40 to the exit for Hector Road. From the Hector Road exit, travel continues south to the National Trails Highway, then east approximately one mile to County Road 20796, then south for 2.2 miles on County Road 20796 to an unnamed dirt road bearing east for another 1.1 miles to the mine office and plant site at the Project.
The Project area operates with electricity and is well served by other infrastructure, including I-40 and the main Burlington Northern Santa Fe (“BNSF”) rail line that runs from Chicago, Illinois to Los Angeles, California running immediately north alongside I-40. There are three main natural gas transmission lines along the I-40. The two southern transmission lines are owned and operated by SCE, while the northern transmission line is owned and operated by Kinder Morgan. The port of Los Angeles, Long Beach and San Diego are all within a half-day drive from the Project on major highways. The Project will likely attract personnel from the Barstow-Victorville area.
The Project deposit is in a prospective area for borate and lithium mineralization and is fundamental to our strategy to become a globally integrated supplier of borates, lithium carbonate and advanced boron derivatives. The deposit mineralization is colemanite and the Project has a similar geological setting to RTB’s Boron open-pit mine and Nirma Limited’s Searles Lake operations, situated approximately 75 miles west-northwest and 90 miles northwest of the Project, respectively.
Mineral Title
We own fee simple (private) lands in Sections 25 and 36 of Township 8 North, Range 5 East of the San Bernardino Principal Meridian. An electrical transmission corridor, operated by SCE, tracts from the northeast to the southwest through the fee lands with SCE having surface and subsurface control to a depth of 500 feet, affecting approximately 91 acres of surface lands in the two sections. While this limits surface access to the land, mineralization remains accessible as the ore body occurs at depths greater than 1,000 feet.
We currently hold 30 unpatented lode claims, 117 unpatented placer claims, and two unpatented millsite claims with the BLM within the U.S. Department of the Interior. Two lode claims were originally filed by Duval Corporation (“Duval”) in 1978 with the other 28 lode claims filed by the Company in January and August 2025. Placer claims were filed between October 29, 2016, and February 24, 2017. A review of the BLM Mineral & Land Record System database shows claim status as filed with next assessment fees due annually on September 1.
Lastly, 272 acres of land located in Section 36 of Township 8 North, Range 5 East of the San Bernardino Principal Meridian, are split estate, with the surface estate owned by us and the mineral estate is owned by the State of California. These lands are available to us through a mineral lease from the California State Lands Commission. We own the remaining lands, with the minerals underlying the transmission line available subsurface.
Overview of Mining Locations
Fort Cady History
Discovery of the Project borate deposit occurred in 1964 when Congdon and Carey Minerals Exploration Company found several zones of colemanite, a calcium borate mineral, between the depths of 1,330 feet to 1,570 feet below ground surface in Section 26. In September 1977, Duval initiated land acquisition and exploration activities near Hector, California. By March 1981, Duval had completed 34 exploration holes, plus one potential water well. After evaluation of the exploration holes, Duval considered several mining methods. Subsequent studies and tests performed by Duval indicated that in-situ mining technology was feasible.
Duval commenced limited testing and pilot-scale solution mining operation in June 1981. Mountain States Mineral Enterprises, Inc. (“MSME”) purchased the Project from Duval in 1985. In July 1986, tests were initiated by MSME, where dilute hydrochloric acid solution was injected into the ore body. The acid dissolved the colemanite and was then withdrawn from the same well. Between 1981 and 2001, the various owners of the Project drilled an additional 17 wells, which were used for a series of injection testing and pilot-scale operations.
An additional phase of pilot plant operations was conducted between 1987 and 1988. The test results were positive; thus, the Project was viewed as commercially viable. MSME sold the Project to Fort Cady Mineral Corporation (“FCMC”) in 1989. In preparation for the permitting process, feasibility studies, detailed engineering and test work were completed by FCMC.
In 1990, a Plan of Operations (“PoO”) was submitted to the BLM and a Mining Conditional Use Permit and Reclamation Plan was submitted to San Bernardino County, which triggered environmental review under NEPA and CEQA. With the Project located on both public and private lands, the public lands are managed by the BLM in accordance with Surface Management Regulations of the Federal Land Policy and Management Act and federal environmental laws, and the private lands administered by San Bernardino County Land Use Services (“SBC-LUS”) in accordance with the California Surface Mining and Reclamation Act, the County Development Code and state environmental laws.
Based upon the activities described in the PoO, under the NEPA regulations, the BLM determined that an EIS was required while under CEQA, SBC-LUS determined that an Environmental Impact Report (“EIR”) was required. Under a Memorandum of Understanding, the two agencies completed a joint EIS and EIR to satisfy their environmental review requirements under NEPA and CEQA, respectively. The EIS and EIR process followed clearly defined requirements for public participation in studies, such as threatened and endangered species, cultural resources, light, noise, and impacts to local communities. The studies were completed, as was the public participation process, which resulted in a 1994 ROD from the BLM that approved the PoO and approval of the Mining Conditional Use Permit and Reclamation Plan from the SBC-LUS.
A second phase of pilot plant operations occurred between 1996 and 2001, during which approximately 2,200 tons of a synthetic colemanite product, marketed as CadyCal 100, were produced. Commercial-scale operations were not commissioned due to low product prices and other priorities of the controlling entity. For many years, boron was used in traditional applications such as cleaning supplies and ceramics, which did not formulate into a strong pull-side demand investment thesis where pricing justified further development of the Project.
In 2017, a group of Australian investors identified the Project and formed the investment thesis that the boron market had similar dynamics to the lithium market a decade earlier. Like the lithium market ten years prior, the market was dominated by a few companies with a compelling pull-side demand growth story fueled by future-facing applications targeting decarbonization and critical materials. Prior to lithium-ion batteries and electric vehicles, lithium was used in traditional everyday applications like boron’s use in recent years. As a result of the investment thesis that boron is expected to experience a supply deficit relative to demand, the group of Australian investors formed ABR and issued shares to Atlas Precious Metals in exchange for Fort Cady (California) Corporation, the entity holding the permits, mineral and property rights of the Project. In 2017, ABR underwent an initial public offering on the ASX and progressed exploration and development of the Project. In September 2021, ABR created a subsidiary, 5E Advanced Materials, Inc., and through the Scheme, reorganized the Company which placed the Company at the top of the corporate structure. Upon 5E Advanced Materials, Inc. becoming the parent company of the organization, in March 2022, we direct listed on the Nasdaq and became an issuer with the U.S. Securities and Exchange Commission.
In total, we have spent in excess of $156 million on the Project thus far, including resource drilling, monitoring wells, metallurgical test works, well injection tests, permitting activities, construction and operation of the SSF, pilot-scale test works and engineering of the commercial-scale facility.
Access and Infrastructure
We continue to develop operating infrastructure for the Project in support of extraction and processing activities. A manned gate is located on the Project access road and provides required site-specific safety briefings and monitors personnel entry and exit to the site. Personnel are predominantly sourced from the surrounding area including Barstow, California and Victorville, California.
The BNSF rail line from Las Vegas, Nevada to Los Angeles, California runs parallel to I-40 and adjacent to the Project. A rail loadout is located approximately 1.2 miles north of the National Trails Highway on a road that bears north and located 0.4 miles west of San Bernardino County Road 20796. San Bernardino County operates six general aviation airports with the closest airport to the Project being the Barstow-Daggett Airport located approximately 23 miles west of the Project off the National Trails Highway. Commercial flight service is available through five airports in the greater Los Angeles area and in Las Vegas, Nevada. A dedicated cargo service airport is located approximately 65 miles southwest of the Project.
The construction of the SSF was performed by a construction contractor with additional local resources supporting construction contracting, construction materials, energy sources, employees, and housing. The Project has good access to I-40 which connects it to numerous sizable communities between Barstow, California and the greater Los Angeles area offering excellent access to transportation, construction materials, labor, and housing. The Project was successful in removing natural gas generators from the facility and is currently supplied by approximately one mega watt of shore power that is sufficient for mine office, storage facilities on site, and the operation of the SSF. An electrical transmission corridor operated by SCE extends northeastward through the eastern part of the Project. The Project has two water wells located nearby to support in-situ leaching operations where unpatented millsite claims are filed. Currently there is no natural gas connects to the Project, but we have a proposal from a major U.S. interstate natural gas transmission system operator to connect to the Mojave Pipeline. Two other natural gas transmission lines run along I-40 near the Project.
The plant site currently has a 1,600 square foot mine office building, a control room, storage buildings, an analytical laboratory, an approximately 20-acre production facility (the SSF), four injection/recovery wells, and an intended gypsum storage area occupying 17 acres. Gypsum is a byproduct of past pilot plant production and is intended, along with calcium chloride, to be a future co-product that can be sold to the regional market.
Project Permits and Reclamation Requirements
We currently have the following Project permits in place:
The MDAQCD has issued operating permits for the SSF and the permits are renewed annually. After front-end engineering and design and during detail design of the proposed commercial-scale facility, and once we have determined each original equipment manufacturer for major pieces of equipment and based on the specification sheets for each piece of equipment, ATC permits for the proposed commercial-scale facility will be provided to MDAQMD for approval. It is expected that the issuance of the ATCs will require that the existing operating permits for the SSF be closed. The ATC permits for the proposed commercial-scale facility must meet National Ambient Air Quality Standards (“NAAQS”) and MDAQMD requirements (Air Resources Board, MDAQMD, and EPA).
There is no reclamation or closure requirement under MDAQMD.
The LRWQC issued the current WDR in 1988. The WDRs regulate activities in the existing surface impoundments, which were used in the 1990’s to produce CadyCal and are no longer being used. We remain compliant with the permit by complying with the monitoring requirements and submitting quarterly reports. A Final Permanent Closure Plan has been approved by the LRWQCB for closure of the existing impoundments. Closure of the ponds and 1988 WDRs is expected to be finalized later in 2025 or 2026. The current proposed commercial-scale facility design includes approximately 37 acres of evaporation ponds for the purpose of removing sodium and calcium from the back end of the processing plant. We will apply for a new or amended WDRs order from LRWQCB for the proposed commercial-scale facility.
There is an existing reclamation and closure requirement approved by LRWQCB. The bond amount to close the ponds is included in the SBC – LUS Financial Assurance Cost Estimate (“FACE”), discussed below. This is currently a certificate of deposit.
The LRWQCB also issued a NONA, verifying that the Project does not require a stormwater permit for approved construction and operations activities. The NONA was issued as the Project is located in a closed basin with no stormwater discharge.
There is no reclamation or bonding requirement associated with the NONA.
SBC-LUS issued the Mining Conditional Use Permit and Reclamation Plan in 1994, based upon the 1990 application and ensuing EIR. The Reclamation Plan was amended, and the permit was modified in 2019 to address changes such as relocation of the processing plant and additional water related infrastructure. Ground use is regulated in accordance with applicable state law. The Mining Conditional Use Permit and Reclamation Plan includes Conditions of Approval for engineering and planning related activities, as well as requirements to avoid impacts to desert tortoises. The permitted production throughput under the Mining Conditional Use Permit is 90,000 short tons of boron oxide or boron oxide equivalent.
We maintain a certificate of deposit with the California State Mining and Reclamation Agency, as administered by SBC-LUS. The FACE is updated annually. The FACE includes demolition of all existing structures, regrading, and revegetation of all disturbance on private lands. This bond also includes plugging and abandonment of all wells located outside the EPA UIC purview.
The BLM issued a ROD in 1994, establishing the EIS boundary. The ROD authorizes mining of borates. The ROD also has requirements for our activities to eliminate adverse impacts to desert tortoises and cultural resources.
Reclamation and land disturbance for BLM is currently included with the FACE on file with the County and bonded in certificate of deposit with the California Division of Mine Reclamation.
The EPA retains primacy for Class 3 solution mining UIC permits in the State of California. The EPA issued the UIC permit for the Project in August 2020. The permit defines the Area of Review (“AOR”) boundary. All subsurface solution mining activities, including monitoring wells and injection wells, are located within the AOR boundary. The EPA approved mining operations in November 2023.
In accordance with the permit conditions, we have installed five upgradient and four downgradient monitor wells for the initial mining block. As a condition to receive final approval in November 2023, the EPA required modification to the permit and the installation of three additional water monitoring wells. The permit was modified in June 2024, and the three additional wells were installed in fall 2024.
We installed four Injection/Recovery Wells (“IR Wells”) and subsequently modified the permit to include horizontal wells. In July 2025, two of the IR Wells were converted from vertical wells to horizontal-side tracks where each well extends approximately 1,500 ft laterally. We expect to submit a final mine plan to the EPA for review based on the performance of the horizontal-side track IR Wells.
We have submitted and maintains a fully collateralized surety bond with the EPA for plugging and abandonment of all wells within the EPA AOR boundary.
Additional environmental permitting that will likely be required for the proposed commercial-scale facility includes:
a.
The California Unified Control Act/Agency has primacy over EPA’s Tier II reporting requirements. The Hazardous Material Business Plan has been submitted for construction related activities and will be updated with processing related chemicals that are expected to be utilized to operate the proposed commercial-scale facility. Such updates will require additional approvals.
SSF Update
In April 2024, we commenced operation of the SSF, an above ground chemical plant designed to refine borates, which has served as a foundation for the design, engineering, and cost optimization for our proposed commercial-scale facility and complex, as well as serving as the source of product for our customer qualification and offtake agreement efforts. The SSF is an essential step in the overall Project development plan and serves as our current extraction and processing facility to demonstrate product development and design. Shortly after we began to process the PLS at the SSF we produced our first batch of boric acid. During July 2024, we sent out our first samples of boric acid produced at the SSF to potential customers, and during April 2025, we were notified by a leading global specialty glass manufacturer that they had successfully produced specialty glass utilizing our boric acid. As of September 2025, we were aware of approximately 14 customers in 8 diverse market segments who had successfully qualified our boric acid through a combination of laboratory evaluation, field trials and truckload-scale shipments. As part of ongoing customer qualification program, we plan to deliver larger volumes of boric acid from the SSF to customer production facilities for product validation. We believe that the progress observed in our customer qualification efforts will facilitate discussions with stakeholders about funding options for Phase 1 of the commercial facility and securing commercial contracts for our future products. The SSF currently produces approximately one short ton per day of boric acid. We plan to continue to run the SSF to refine our operations, more effectively optimize detail engineering of our proposed commercial-scale facility, and to produce boric acid for customer qualification.
Preliminary Feasibility Study
In August 2025, we issued our PFS that was prepared in accordance with Regulation S-K 1300, which focused on Phase 1 development of our Fort Cady Project to develop a 130,000 short ton per annum boric acid plant. We believe the PFS demonstrates a world-class resource and reserve, management’s firm understanding and direction for the business, which can position the company to achieve profitability, generate cash flow, and reduce risk. The PFS includes a revised mineral resource estimate and mineral reserve statement for boric acid, estimates for capital costs and operating expenses, and a bottoms-up economic analysis of the first commercial phase of the Project. The financial model for the economic analysis includes third-party preliminary market studies and independent pricing forecasts for boric acid, calcium chloride and gypsum. The report was prepared by qualified persons (“QP” as defined in S-K 1300) including Company management and third-party independent companies Miocene, Fluor, Geomega, Inc., and
Escalante Geological Services, LLC (“Escalante”). All QPs have the necessary experience per Regulation S-K 1300 and material assumptions and information pertaining to the disclosure of our mineral resources, including material assumptions relating to all modifying factors, price estimates, and scientific and technical information, as described in the PFS, and remain current as of the date of this report.
The PFS converted approximately 41% of our total resource and established approximately 5.3 million short tons of boric acid reserves with an average grade of 8.03% (B 2 O 3) and an initial 39.5 year life of mine utilizing an ISL mining method. The PFS allows for optionality for future expansion phases to develop and convert the remaining portions of our total resource into reserves and future endeavors into value added advanced boron derivatives and economically accretive byproducts.
The financial model for the economic analysis included in the PFS was based upon a third-party preliminary market study which evaluated future supply and demand thematics for the boric acid market, as well as capital estimates developed by our EPC firm, Fluor and Miocene. The PFS included a capital estimate of approximately $367 million, a 15% contingency of approximately $55 million, and owner’s costs of approximately $13 million, for an aggregate capital estimate of approximately $435 million. The capital estimate includes the anticipated costs for a natural gas CHP COGEN facility that will power Phase 1 of the Project.
We will continue to operate the SSF while we stage gate to FEL-3 engineering for Phase 1 of the commercial-scale complex
FEL-3 engineering is expected to provide the necessary estimates to publish a final feasibility study and a final investment and construction decision for Phase 1 of the proposed commercial-scale complex. Based upon progress to date, we are now targeting to reach initial commercial production from Phase 1 in the second half of calendar year 2028.
Plan of Operations
Upon successful development of the Project, we expect to mine and process colemanite to produce borates, calcium chloride and gypsum. The borates produced are planned to be further produced into second, third and fourth boron derivatives. Initially, we expect to derive revenue principally from the sale of boric acid, calcium chloride, and gypsum. As our advanced boron materials strategy develops, we intend to produce revenue from advanced boron materials further enabling decarbonization, energy, food security, and defense applications.
The Project deposit is planned to be mined via ISL mining to recover leached solution from the mineralized horizons, which is a technique that has been utilized for several decades in the production of uranium, salt, bromine, potash and soda ash. The use of in-situ technology for boron extraction was developed at the Project property in the 1980s. In-situ solution mining depends on void spaces, porosity, permeability, ore zone thickness, transmissivity, storage coefficient, piezometric surface, and hydraulic gradient as well as reaction and extraction method efficiencies. There are various ways of developing the wellfield for in-situ leaching, including a “push-pull” mechanism where wells function as both injection and recovery wells; line drive; and multiple spot patterns. We plan to develop the Project utilizing a horizontal well development strategy, and this strategy was incorporated into the assumptions for the PFS. During July 2025, we converted two of our existing vertical IR Wells into horizontal wells by drilling 1,500-foot laterals from each well, placing the wellbores in high-grade colemanite zones of the deposit. We plan to operate these horizontal wells for the next several months to optimize the wellfield design and operational methods for the proposed commercial-scale facility.
The recovery of boron from colemanite is currently occurring through ISL mining and boric acid is being produced at the SSF. The in-situ mining method includes injecting a weak hydrochloric acid (“HCl”) solution (containing <5% HCl in substantially recycled water solution with regenerated HCl) through wells drilled into the colemanite ore body. The injected acid remains in the formation for a limited period of time to allow reaction with the alkaline ore body and leach the colemanite ore.
The extracted solution is pumped to the processing facility where leach solution is crystallized to produce boric acid. The crystallized boric acid is dried, sized, and bagged as final product. Other boron products are expected to be prepared for market, as required, by end-use customers. Calcium is expected to be recovered from the remaining solution after boric acid processing to produce either gypsum or calcium chloride with the final solution being substantially recycled back into the resource deposit. Within the processing facility, some HCl is regenerated from the gypsum precipitation process as a result of the sulfuric acid acidification of the process recycle stream. The weak HCl solution is combined with recycled water to produce the make-up solution for reinjection into the formation. The process operates a zero liquid discharge evaporator and produces no liquid waste.
Mineral Resource Estimate
In March 2025, Mr. Steven Kerr of Escalante completed and updated resource estimate for the Project. The March 2025 resource estimate updated the prior estimate from 2021, and incorporated data from three additional bore holes and the acquisition of additional mineral tenure for the Project which occurred during the intervening period. That report identified a measured plus indicated mineral resource estimate of 109.13 million short tons under mineral control by the Company, containing an average grade of 7.89% B 2 O 3 and 303 parts per million (“ppm”) of lithium, using a 2.0% cut-off grade for B 2 O 3. The mineral resource estimate also identified 3.35 million short tons of inferred resources under mineral control by the Company. Uncontrolled land (State of California Surface) contained approximately 22.36 million short tons of measured plus indicated resources and an inferred resource of 0.93 million short tons. The electrical transmission corridor operated by SCE contained 27.78 million short tons, or 25%, of the total mineral resources. While SCE maintains control of the surface and resources to a depth of 500 ft, it does not impinge on our mineral rights for colemanite which occur at depths greater than 1,000 ft. The mineral resource estimate was incorporated into our PFS, which is incorporated by reference to Exhibit 96.1 to this Annual Report on Form 10-K.
Mineral Resources
Regulation S-K 1300 defines a “mineral resource” as a concentration or occurrence of material of economic interest in or on the Earth’s crust in such form, grade or quality, and quantity that there are reasonable prospects for economic extraction. A mineral resource is a reasonable estimate of mineralization, considering relevant factors such as cut-off grade, likely mining dimensions, location, or continuity, that, with the assumed and justifiable technical and economic conditions, is likely to, in whole or in part, become economically extractable. It is not merely an inventory of all mineralization drilled or sampled.
A “measured mineral resource” is that part of a mineral resource for which quantity and grade or quality are estimated on the basis of conclusive geological evidence and sampling. The level of geological certainty associated with a measured mineral resource is sufficient to allow a qualified person to apply modifying factors, as defined in this section, in sufficient detail to support detailed mine planning and final evaluation of the economic viability of the deposit. Because a measured mineral resource has a higher level of confidence than the level of confidence of either an indicated mineral resource or an inferred mineral resource, a measured mineral resource may be converted to a proven mineral reserve or to a probable mineral reserve.
An “indicated mineral resource” is that part of a mineral resource for which quantity and grade or quality are estimated on the basis of adequate geological evidence and sampling. The level of geological certainty associated with an indicated mineral resource is sufficient to allow a qualified person to apply modifying factors in sufficient detail to support mine planning and evaluation of the economic viability of the deposit. Because an indicated mineral resource has a lower level of confidence than the level of confidence of a measured mineral resource, an indicated mineral resource may only be converted to a probable mineral reserve.
An “inferred mineral resource” is that part of a mineral resource for which quantity and grade or quality are estimated on the basis of limited geological evidence and sampling. The level of geological uncertainty associated with an inferred mineral resource is too high to apply relevant technical and economic factors likely to influence the prospects of economic extraction in a manner useful for evaluation of economic viability. Because an inferred mineral resource has the lowest level of geological confidence of all mineral resources, which prevents the application of the modifying factors in a manner useful for evaluation of economic viability, an inferred mineral resource considered when assessing the economic viability of a mining project must be presented along with economic viability excluding inferred resources and may not be converted to a mineral reserve.
Resource Assumptions
Key assumptions used in the resource estimate include: mineralized horizons exhibit lateral continuity that will support mining using in-situ leaching mining methods, mineralized horizons are not disrupted by structural or stratigraphic features that could limit mining, there is reasonable continuity of colemanite mineralization throughout the deposit, and there is adequate exploration data to support estimation of resources.
Resource Methodology
The database used for resource estimation includes 52 core holes and three rotary holes for a total of 55 bore holes. Thirty of the core holes were completed by Duval between 1979 and 1981. We completed 14 core holes in 2017 and another core hole in 2022. In 2024, we completed three additional rotary holes as observation wells from which chip samples were collected through the mineral horizons for B 2 O 3 and lithium analyses. The cumulative sampled length for the database is approximately 17,848 feet. The Project’s exploration dataset is current as of February 12, 2025. Drilling coordinates in the database are in UTM NAD 83-11, and depths and elevations are reported in meters. Borate is listed as weight percent (%) B 2 O 3 and lithium as ppm. The drilling database contains 5,767 analytical values for B 2 O 3 and 5,402 analytical values for lithium.
Core recovery for the 2017 drilling program ranged from 93% to 100% with an overall average of 97.60%. Physical core recovery records for earlier drilling conducted by Duval and FCMC are not available, but based on missing intervals in the drilling database, core recovery likely exceeded 90% in the core drilling and correlates to the 2017 drilling program. The QP has completed a thorough review and verification of the drilling database and found the database to be sufficient for resource modeling.
The QP developed a gridded geologic model of the Project using Carlson Mining™ software. The mineralization does not correlate to lithological markers as the entire sequence is predominantly lacustrine mudstone. However, detailed examination of the analytical results reveals distinct mineralized horizons. The deposit was delineated based on these patterns of mineralization into four mineralized horizons, two non-mineralized or weakly mineralized interbeds and two non-mineralized horizons bounding the deposit. The grid model was constructed across the deposit area, with a grid cell size of 50 meters by 50 meters. Grids represent the bounding elevation surfaces of key horizons, horizon thicknesses, and analytical grades. Grids representing the bounding surface elevations of the mineral horizon were interpolated through triangulation. Mineral horizon grids for thickness and analytical grades were interpolated using Ordinary Kriging (“OK”) and Inverse Distance Squared (“ID2”) algorithms. Mineralization is spatially defined by a resource boundary using a distance of 200 meters from the last intersection of mineralization in a drill hole and by property boundaries. Grids are masked to the outside of the resource boundary.
Using composites for each mineralized horizon, variography was successful for B 2 O 3 grades for the Major Mineralized Horizon (“MMH”), Intermediate Mineralized Horizon (“IMH”), and the Lower Mineralized Horizon (“LMH”). Variogram modeling was unsuccessful for the Upper Mineralized Horizon (“UMH”) and with lithium in all horizons. Grids representing B 2 O 3 grades for the MMH, IMH, and LMH were constructed using OK based on the constructed variograms. ID2 interpolation was used with all remaining grade grids using the same spatial limits established with the horizon grids.
Cut-off Grade
Cut-off grade is an economic analysis to measure cash costs (i.e., the variable cost to produce boric acid compared to the price that can be achieved in the market for the sale of boric acid). We commenced mining operations in January 2024 and began operating the SSF in April 2024. The SSF achieved a steady state of operation in the summer of 2024 and optimized mining operations by September 2024. As such, mining data from September and October 2024 have been utilized as the basis of design and further leveraged for the cut-off grade analysis. Using this data set, an in-depth assessment was performed that included an analysis of the cash costs (i.e., the variable cost to produce boric acid) and excluded book costs (i.e., depreciation) as the capital is assumed to have already been invested to build the project such that it can operate. The definition of cut-off grade for the in-situ mining operation is the point at which the Company would cease operating a particular well or in the case of a combination of wells, the wellfield. As such, cash costs are established as the basis for the analysis.
A 5.0% B 2 O 3 cut-off grade was previously established by Duval and was carried forth by previous QPs in previous technical report summaries. An in-depth assessment of cut-off grade was undertaken in 2022 and 2023 as mass and energy balances were developed to fundamentally begin to assess economic viability of the Project. Data informing the mass and energy balances included incorporating the results of leaching tests, historical results, mining, and processing costs, as well as commodity pricing, and resulted in a 2.0% cut-off calculation.
The in-depth analysis discussed above incorporated mineralization and at what point economic extraction or boron in solution is no longer viable. The driver of this analysis focuses on three specific ratios derived from the basis of design using mining data from the periods of September and October 2024: calcium to boron, sodium to boron, and magnesium to boron. These three ratios are drivers of various costs, chemical utilizations, and byproduct production rates. For example, calcium to boron impacts sulfuric acid utilization and gypsum production compared to boric acid production. Additionally, magnesium to boron impacts lime utilization and metal salt waste production compared to boric acid production. Lastly, sodium to boron impacts HCl utilization and sodium chloride production compared to boric acid production.
The PFS incorporated the above methodology and other key assumptions that are in the financial model detailed in Section 19 of the PFS (refer to Exhibit 96.1 hereto). The sales price for boric acid has increased over the past several years and was tracking around $1,100 to $1,300 per short ton free on board (“FOB”) in the spot market during June and July of 2025, and the PFS includes an assumption of $1,248 per short ton FOB when production first commences based on a preliminary market study prepared by an independent third-party. Sales prices for calcium chloride and gypsum in the PFS were similarly based upon a preliminary market study and forecasts prepared by the same independent third-party. The result of this exercise is a 2.0% financially viable driven grade cut-off, where the costs are near the forecasted price for boric acid.
Fort Cady Mineral Resource Estimate as of March 10, 2025
Results of the mineral resource estimation are shown in the table below, based on resource classification of the Project. The resource estimate contains a combined 109.13 million short tons of measured plus indicated resources with an average grade of 7.89%
B 2 O 3 and 303 ppm lithium, using a 2.0% cut-off grade for B 2 O 3 and no cut-off grade for lithium. The sales price for boric acid has increased over the past several years and was tracking around $1,100 to $1,300 per short ton FOB in the spot market during June and July of 2025. Our PFS estimates the FOB prices for boric acid, calcium chloride and gypsum to be $1,248, $174 and $33 per short ton, respectively, in the first year of production, based upon a preliminary market study prepared by an independent third-party, as discussed in further detail of Section 16 and 19.3.1 of our PFS filed as Exhibit 96.1 hereto. The mineral resource estimate also identifies 4.29 million short tons of total inferred resources with an average grade of 7.45% B 2 O 3 and 310 ppm lithium. The reference point for the resource in the PFS is in-situ prior to mining losses and processing losses. The resource estimate detailed below, including all assumptions and inputs utilized to arrive at such estimate, remain reasonable and accurate as of June 30, 2025.
| Thick · B203 · H3BO3 · Li · LCE · Resource Classification Tons · Product Tons - Measured · Product Tons - Indicated · Product Tons - Inferred | ||||||||||||||||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Property · Bed(1) · (m) · (%) · (%) · (ppm) · (%) · Tonnes · Tons · Measured · Indicated · Inferred · B2O3 · H3BO3 · LCE · B2O3 · H3BO3 · LCE · B2O3 · H3BO3 · LCE | ||||||||||||||||||||||||||||||||||||||||||
| UMH | 1.29 | 6.95 | 12.34 | 305.2 | 0.16 | 1,019,259 | 1,123,540 | 134,825 | 988,715 | — | 9,370 | 16,642 | 219 | 68,716 | 122,039 | 1,606 | — | — | — | |||||||||||||||||||||||
| Unpatented | MMH | 5.81 | 8.53 | 15.15 | 382.3 | 0.20 | 4,604,120 | 5,075,172 | 609,021 | 4,466,151 | — | 51,949 | 92,262 | 1,239 | 380,963 | 676,590 | 9,089 | — | — | — | ||||||||||||||||||||||
| Lode Claims | IMH | 10.02 | 6.66 | 11.82 | 334.1 | 0.18 | 7,930,744 | 8,742,146 | 1,049,058 | 7,693,089 | — | 69,824 | 124,008 | 1,866 | 512,046 | 909,393 | 13,681 | — | — | — | ||||||||||||||||||||||
| LMH | 5.18 | 9.42 | 16.73 | 252.7 | 0.13 | 4,097,952 | 4,517,217 | 542,066 | 3,975,151 | — | 51,069 | 90,698 | 729 | 374,505 | 665,121 | 5,348 | — | — | — | |||||||||||||||||||||||
| Sub-Total | 17,652,074 | 19,458,075 | 2,334,969 | 17,123,106 | — | 182,213 | 323,610 | 4,053 | 1,336,229 | 2,373,143 | 29,724 | — | — | — | ||||||||||||||||||||||||||||
| Fee Land | UMH | 2.96 | 6.60 | 11.72 | 250.6 | 0.13 | 5,239,482 | 5,775,538 | 1,443,885 | 4,216,143 | 115,511 | 95,296 | 169,246 | 1,926 | 278,265 | 494,199 | 5,624 | 7,624 | 13,540 | 154 | ||||||||||||||||||||||
| MMH | 15.25 | 8.23 | 14.62 | 323.0 | 0.17 | 26,950,960 | 29,708,340 | 7,427,085 | 21,687,088 | 594,167 | 611,249 | 1,085,578 | 12,770 | 1,784,847 | 3,169,889 | 37,289 | 48,900 | 86,846 | 1,022 | |||||||||||||||||||||||
| IMH | 6.09 | 7.24 | 12.85 | 349.4 | 0.19 | 10,770,455 | 11,872,391 | 2,968,098 | 8,666,845 | 237,448 | 214,781 | 381,451 | 5,520 | 627,160 | 1,113,837 | 16,119 | 17,182 | 30,516 | 442 | |||||||||||||||||||||||
| LMH | 8.11 | 8.63 | 15.33 | 222.9 | 0.12 | 14,330,824 | 15,797,025 | 3,949,256 | 11,531,828 | 315,941 | 340,831 | 605,316 | 4,686 | 995,227 | 1,767,523 | 13,682 | 27,266 | 48,425 | 375 | |||||||||||||||||||||||
| Sub-Total | 57,291,720 | 63,153,293 | 15,788,323 | 46,101,904 | 1,263,066 | 1,262,157 | 2,241,592 | 24,902 | 3,685,500 | 6,545,448 | 72,714 | 100,973 | 179,327 | 1,992 | ||||||||||||||||||||||||||||
| Power Corridor | UMH | 2.57 | 5.91 | 10.50 | 2.7 | 0.00 | 2,094,642 | 2,308,947 | 415,611 | 1,731,711 | 161,626 | 24,563 | 43,623 | 6 | 102,344 | 181,763 | 25 | 9,552 | 16,965 | 2 | ||||||||||||||||||||||
| MMH | 22.06 | 7.83 | 13.91 | 277.0 | 0.15 | 17,965,945 | 19,804,059 | 3,564,731 | 14,853,044 | 1,386,284 | 279,118 | 495,714 | 5,256 | 1,162,993 | 2,065,476 | 21,900 | 108,546 | 192,778 | 2,044 | |||||||||||||||||||||||
| IMH | 4.40 | 5.09 | 9.04 | 279.0 | 0.15 | 3,580,525 | 3,946,852 | 710,433 | 2,960,139 | 276,280 | 36,168 | 64,234 | 1,055 | 150,699 | 267,642 | 4,396 | 14,065 | 24,980 | 410 | |||||||||||||||||||||||
| LMH | 4.25 | 7.83 | 13.90 | 250.0 | 0.13 | 3,461,337 | 3,815,470 | 686,785 | 2,861,603 | 267,083 | 53,754 | 95,466 | 914 | 223,973 | 397,776 | 3,808 | 20,904 | 37,126 | 355 | |||||||||||||||||||||||
| Sub-Total | 27,102,450 | 29,875,328 | 5,377,559 | 22,406,496 | 2,091,273 | 393,602 | 699,038 | 7,231 | 1,640,010 | 2,912,658 | 30,129 | 153,068 | 271,848 | 2,812 | ||||||||||||||||||||||||||||
| Total | 102,046,244 | 112,486,697 | 23,500,851 | 85,631,507 | 3,354,339 | 1,837,973 | 3,264,240 | 36,186 | 6,661,739 | 11,831,248 | 132,567 | 254,040 | 451,175 | 4,804 | ||||||||||||||||||||||||||||
| CA Surface | UMH | 4.78 | 6.99 | 12.41 | 313.2 | 0.17 | 3,788,533 | 4,176,141 | 167,046 | 3,842,050 | 167,046 | 11,676 | 20,737 | 279 | 268,559 | 476,961 | 6,406 | 11,676 | 20,737 | 279 | ||||||||||||||||||||||
| Section 36 | MMH | 14.02 | 6.76 | 12.01 | 376.0 | 0.20 | 11,109,308 | 12,245,912 | 489,836 | 11,266,239 | 489,836 | 33,113 | 58,809 | 980 | 761,598 | 1,352,598 | 22,549 | 33,113 | 58,809 | 980 | ||||||||||||||||||||||
| (Uncontrolled) | IMH | 4.88 | 3.66 | 6.50 | 340.3 | 0.18 | 3,869,439 | 4,265,325 | 170,613 | 3,924,099 | 170,613 | 6,243 | 11,088 | 309 | 143,590 | 255,016 | 7,109 | 6,243 | 11,088 | 309 | ||||||||||||||||||||||
| LMH | 2.98 | 6.18 | 10.98 | 465.9 | 0.25 | 2,358,930 | 2,600,274 | 104,011 | 2,392,252 | 104,011 | 6,431 | 11,422 | 258 | 147,921 | 262,708 | 5,933 | 6,431 | 11,422 | 258 | |||||||||||||||||||||||
| Uncontrolled Total | 21,126,210 | 23,287,653 | 931,506 | 21,424,641 | 931,506 | 57,464 | 102,056 | 1,826 | 1,321,669 | 2,347,283 | 41,996 | 57,464 | 102,056 | 1,826 | ||||||||||||||||||||||||||||
Table prepared using a 2.0% B 2 O 3 cut-off grade and no lithium cut-off grade.
(1)
“UMH” is Upper Mineralized Horizon, “MMH” is Major Mineralized Horizon, “IMH” is Intermediate Mineralized Horizon, and, and “LMH” is Lower Mineralized Horizon.
Commodity Pricing Assumptions
Our PFS includes an economic analysis, and we obtained an independent preliminary market study for boric acid, calcium chloride and gypsum. The preliminary market studies were based on 15 years of historical data and include an assessment of future supply and demand analysis as well as forecasted future price assumptions, as further detailed in Sections 16 and 19.3.1 of our PFS, which is incorporated by reference as Exhibit 96.1. Our PFS estimates the price for boric acid to be $1,248 per short ton in the initial year of commercial production, escalating to $1,364 per short ton in 2033 due to demand outpacing supply of boric acid, and then held flat when supply and demand for boric acid are expected to normalize. Our PFS estimates the price for calcium chloride and gypsum to be $174 and $33 per short ton, respectively, in the initial year of commercial production, with such prices held flat throughout the model. The price utilized in the financial model for gypsum and calcium chloride is the real price as of June 2025 as provided by the independent preliminary market study. Per the independent preliminary market study, the sales price for boric acid has increased over the past several years and was tracking around $1,100 to $1,300 per short ton FOB in the spot market during June and July of 2025 with variations driven by differing jurisdictions in the spot market. Refer to the tables below for a summary of the prices utilized in our economic analysis included in our PFS.
| Year · 2028 · 2033 · 2067 | |||||
|---|---|---|---|---|---|
| Boric acid price per short ton | $1,248 | $1,364 | $1,364 | ||
| CAGR(1) | 1.8% | 0.2% | |||
| Calcium chloride per short ton | $174 | $174 | $174 | ||
| CAGR(1) | 0.0% | 0.0% | |||
| Gypsum per short ton | $33 | $33 | $33 | ||
| CAGR(1) | 0.0% | 0.0% | |||
| (1) Compounded annual growth rate is calculated based upon the initial price in 2028 for the respective product to the end of the indicated year. | |||||
| Life of Mine Price Assumptions(1) | ||
|---|---|---|
| Measured and Indicated | ||
| Average | Range | |
| Boric acid price per short ton | $1,354 | $1,201 - $1,374 |
| Calcium chloride per short ton | $174 | $174 - $174 |
| Gypsum per short ton | $33 | $33 - $33 |
| (1) The economic analysis in Section 19 of the Preliminary Feasibility Study includes only measured and indicated resources. | ||
The PFS was prepared based primarily on information available at the time of preparation, is subject to assumptions, conditions and is qualified by various limitations. The foregoing summary description of the PFS is qualified in its entirety by reference to the full PFS, which is included as Exhibit 96.1 to this Annual Report on Form 10-K.
Internal Controls Disclosure
Between September 2017 and October 2017, 14 holes for a total of 23,111 feet were completed as part of a confirmatory resource drilling program. Assay results from all 14 drill holes were used in the mineral resource estimate. There are 2,113 samples from the 2017 drilling program representing 1,713 feet of core. In conjunction with the 2017 drilling program, 29 historical drill holes completed by Duval and four holes completed by FCMC were in the mineral resource estimate. There are 3,672 samples from the historic drilling representing a cumulative total of 10,831 feet of core.
The PFS indicates that the quality assurance and quality control (“QA/QC”) procedures for the Duval and FCMC drill holes are unknown, though the work products compiled during these historic drilling campaigns, suggests they were carried out by competent geologists following procedures considered standard practice at those times. Discussions held with the exploration geologist for Duval at the time of drilling and sampling indicate that Duval had internal QA/QC procedures in place to ensure that assay results were accurate. Geochemical analyses were carried out using X-Ray Fluorescence Spectrometry (“XRF”). XRF results were reportedly checked against logging and assay data.
For the database of drill holes, entire core hole sequences were sampled and dispatched by commercial carrier to the Saskatchewan Research Council (“SRC”) for geochemical analysis. As part of the QA/QC procedures, internationally recognized standards, blanks and duplicates were inserted into the sample batches prior to submitting to SRC. SRC has been accredited by the Standards Council of Canada and conforms with the requirements of ISO/IEC 17025.2005. Upon receipt of samples, SRC completed an inventory of samples received, completing the chain of custody documentation, and providing a ledger system tracking samples received and steps in process for sample preparation and analysis. Core samples and chip samples were dried in their original sample bags, then jaw crushed. A subsample was split out using a sample riffler. The subsample was then pulverized with a jaw and ring grinding mill. The grinding mill was cleaned between each sample using steel wool and compressed air or by silica sand. The resulting pulp sample was then transferred to a barcode labeled plastic vial for analysis. All samples underwent a multi-element Inductively Coupled Plasma Optical Emission Spectroscopy (“ICP-OES”), using a multi-acid digestion for a range of elements. Boron was also analyzed by ICP-OES but underwent a separate digestion where an aliquot of the sample was fused in a mixture of NaO 2/NaCO 3 in a muffle oven, then dissolved in deionized water, prior to analysis. Major oxides were reported in weight percent. Minor, trace, and rare earth elements were reported in ppm. The detection limit for boron was 2 ppm and 1 ppm for lithium.
For the database of drill holes, a total of 2,253 core samples and 441 control samples were submitted for multi-element analysis to SRC. We submitted control samples, in the form of certified standards, blanks and coarse duplicates (bags with sample identification supplied for SRC to make duplicate samples). In addition to these control samples, SRC also submitted their own internal control samples in the form of standards and pulp duplicates. Certified standards, prepared by the National Institute of Standards and Technology, were submitted as part of our QA/QC procedures. No two standards in any single batch submission were more than two standard deviations from the analyzed mean, implying an acceptable level of precision of SRC instrumentation. SRC assayed two different standards, for its own QA/QC protocol and the QP found that the analytical precision for analysis of both standards was reasonable, with no two standards in any single batch submission being more than two standard deviations from the analyzed mean.
Blank samples inserted consisting of non-mineralized marble. One hundred and thirty-five blank samples were submitted, all of which had assay results of less than 73 ppm boron. The level of boron detected in the blanks was likely sourced from pharmaceutical (borosilicate) glass used during sample digestion. These boron concentrations are considered immaterial in relation to the boron levels detected in the colemanite mineralization and do not appear to represent carryover contamination from sample preparation. Lithium levels in the blank samples were also at acceptable levels with the majority of assays less than 15 ppm lithium. The four highest lithium levels in the blanks immediately followed samples that contained relatively high lithium concentrations. Overall, the concentration of the primary elements of interest (boron and lithium) in the blank samples were at levels considered to be acceptable, implying a reasonable performance for sample preparation.
A total of 136 duplicate samples were submitted to the SRC. SRC composed coarse duplicate samples using a Boyd rotary splitter. There was a good correlation between original and duplicate samples with a reasonable level of precision maintained in the results.
Comparison of Mineral Resource Estimates to Prior Year
The technical report summary included as an exhibit to our prior year Annual Report on Form 10-K, which was estimated as of April 1, 2023 and remained valid as of June 30, 2024, reported measured, indicated and inferred mineral resources of 2.65, 3.15 and 8.17 million short tons of boric acid, respectively. The mineral resource estimate included as exhibit 96.1 to this Annual Report and summarized above, was estimated as of March 10, 2025 and remained valid as of June 30, 2025, reported measured, indicated and inferred mineral resources of 3.37, 14.18 and 0.55 million short tons of boric acid, respectively. This represents a 203% increase in combined measured and indicated resource, which is comprised of a 27% increase in measured resource, and a 350% increase in indicated resource. Inferred resource decreased 93% compared to the prior year. These year-over-year changes are ascribed to increases in mineral tenure between periods.
Mineral Reserve Estimate
In August 2025, Miocene completed a mineral reserve estimate for the Project. The mineral reserve estimate was developed based upon the detailed mine plan included in Section 13 of our PFS and the mineral resource estimate. Prior to August 2025, we had not yet established mineral reserves and therefore have not disclosed reserve estimates as of June 30, 2025 or 2024. Reserves point of reference is in-situ with a 2% cutoff grade established based on the analysis performed with the mineral resources cut-off grade. Our EPA UIC permit subdivides the mineralized deposit into three blocks for development. Block 1 comprises the northwestern third of the orebody, Block 2 occupies the central portion of the orebody, and Block 3 comprises the southeastern third of the orebody. The SSF currently operates in Block 2 and Block 2 is permitted for mining with sufficient resources on fee-based lands and within the power corridor operated by SCE to convert resources to reserves on an economic basis, which provides for a 39.5 years life of mine. To convert additional resources to reserves, Block 1 and Block 3 would need to be authorized by the EPA and a mine plan devised that includes this mineral tenure.
For economic modeling, a mine plan was designed where recovery and flow rates are sufficient to feed the chemical plant where PLS is converted to a finished refined borate product available for sale. Production output is within permitted parameters with forecasted revenue from borate sales based on a pricing forecast based on the aforementioned third-party preliminary market study.
The mine plan and wellfield optimization were based on third-party engineering work that incorporated 18 months of actual wellfield data from the SSF into the design and included a bottoms-up capital estimate. The capital estimate was derived by Fluor for the inside and outside battery limits above ground and a total capital estimate was derived and incorporated into the economic analysis. The operating costs were derived from material and energy balances provided by Fluor as well as a bottoms-up labor build for human capital requirements. The revenue and cost inputs for the economic model were on a real basis.
The August 2025 reserve estimate identified 1.35 million short tons of proven boric acid reserves, and 3.98 million short tons of probable boric reserves, containing an average grade of 8.03% B 2 O 3 using a 2.0% cut-off grade for B 2 O 3, consistent with the cut-off grade for the mineral resource estimate. The mineral reserve estimate was incorporated into our PFS, which is incorporated by reference to Exhibit 96.1 to this Annual Report on Form 10-K.
Mineral Reserves
Regulation S-K 1300 defines a “proven mineral reserve” as is the economically mineable part of a measured mineral resource and can only result from conversion of a measured mineral resource.
A “probable mineral reserve” is the economically mineable part of an indicated and, in some cases, a measured mineral resource.
Reserve Assumptions
Assumptions utilized for the reserve estimate were consistent with the assumptions utilized for the resource estimate, except that only measured and indicated resource included in the mine plan from fee-based lands and the power corridor operated by SCE were included in the resource base (representing approximately 80% of our fee-based lands and 5% of the power corridor). The economic assessment that supports the recognition of reserves was based on a 130,000 short ton per year boric acid production plant, a capital cost estimate for Phase 1 of the Project of approximately $435 million, in-situ leading mining operation delivering 10.2% boric acid in solution (head grade), by weight, to an above ground processing plant; the aforementioned commodity price assumptions; cash operating costs of approximately $563 per ton of boric acid produced and a 7% discount rate. Additional assumptions included performing a tradeoff analysis based on actual vertical well performance relative to expected horizontal well performance whereby horizontal well performance is expected to outperform vertical wells, the chemical plant is designed to yield 95.1% boric acid yield, leaching efficiency is assumed to be 81.9% based on leach testing, and mining efficiency was 95% based on the Company’s July 2025 horizontal drilling program.
The reserve estimate is subject to potential change based on changes to the forward-looking cost and revenue assumptions. It is assumed that we will produce and sell borates to customers once the proposed commercial-scale facility is constructed, commissioned, and in operation. Full extraction of this reserve is dependent upon the modification of the Company’s UIC permit to include the final mine plan based on the learnings obtained from the Company’s horizontal wells that were drilled in July 2025. We obtained a minor modification and authorization to drill the horizontal and sidetrack program in July 2025, and it is our expectation that we will be successful in modifying the UIC permit. The evaporation ponds incorporated into the design of the proposed commercial-scale facility and placed on our fee-based land require a WDR with the LRWQCB. We have an existing WDR for evaporation ponds and we expect to obtain the WDR for the evaporation ponds to remove calcium and sodium.
We do not believe that there are other existing environmental, permitting, legal, socio-economic, marketing, political, or other factors that might materially affect the in-situ mineral reserve estimate.
Fort Cady Mineral Reserve Estimate as of August 4, 2025
| Probable Mineral Reserves | |||||||
|---|---|---|---|---|---|---|---|
| Bed | Mean Mineralized Bed Thickness (ft) | Avg. B2O3 Grade(wt. %) | Insoluble Material Grade(wt. %) | Mineralized Bed Volume (ft3) | Recoverable Mineralized Bed Volume (ft3) | B2O3 Reserve (tons) | H3BO3 Reserve (tons) |
| UMH | 9.08 | 6.58 | 52.5 | 5,656,611 | 4,401,126 | 168,503 | 299,261 |
| MMH | 61.18 | 8.21 | 56.9 | 36,911,677 | 28,719,130 | 1,099,550 | 1,952,800 |
| IMH | 17.20 | 7.20 | 55.9 | 12,649,669 | 9,842,075 | 376,817 | 669,227 |
| LMH | 20.27 | 8.62 | 54.2 | 20,054,643 | 15,603,515 | 597,401 | 1,060,984 |
| Proven Mineral Reserves | |||||||
|---|---|---|---|---|---|---|---|
| Bed | Mean Mineralized Bed Thickness (ft) | Avg. B2O3 Grade(wt. %) | Insoluble Material Grade(wt. %) | Mineralized Bed Volume (ft3) | Recoverable Mineralized Bed Volume (ft3) | B2O3 Reserve (tons) | H3BO3 Reserve (tons) |
| UMH | 9.08 | 6.59 | 52.5 | 1,924,171 | 1,497,102 | 57,319 | 101,798 |
| MMH | 61.18 | 8.22 | 56.9 | 12,492,985 | 9,720,167 | 372,149 | 660,937 |
| IMH | 17.20 | 7.21 | 55.9 | 4,312,901 | 3,355,652 | 128,476 | 228,173 |
| LMH | 20.27 | 8.62 | 54.2 | 6,839,526 | 5,321,493 | 203,740 | 361,843 |
| Proven and Probable Mineral Reserves | ||||||
|---|---|---|---|---|---|---|
| Reserve | Avg. B2O3 Grade(wt. %) | Insoluble Material Grade(wt. %) | Mineralized Bed Volume(ft3) | Recoverable Mineralized Bed Volume(ft3) | B2O3 Reserve(tons) | H3BO3 Reserve(tons) |
| Proven | 8.03 | 55.7 | 25,569,583 | 19,894,414 | 761,684 | 1,352,751 |
| Probable | 8.03 | 55.7 | 75,272,600 | 58,565,846 | 2,242,271 | 3,982,272 |
Salt Wells Projects
In addition to the Project, we had an Earn-in Agreement with Great Basin Resources Inc. (“Great Basin”) which allowed us to acquire a 100% interest in a salt wells projects (the “Salt Wells Projects”) in the State of Nevada if we incurred certain project related expenditures. The Earn-in Agreement with Great Basin provided for a 3% revenue royalty if concentrates or ores of minerals were sold in the future. During February 2025, we chose not to renew certain mining claims related to the Salt Wells Projects, which effectively terminated the Earn-in Agreement with Great Basin, and we have no further interests in the project.
Available Information
We make available free of charge on our website, www.5eadvancedmaterials.com, our annual reports on Form 10-K, quarterly reports on Form 10-Q, current reports on Form 8-K and amendments to those reports filed or furnished pursuant to the Exchange Act, as soon as reasonably practicable after we electronically file such information with, or furnish it to, the SEC. These documents are also available on the SEC’s website atwww.sec.gov. The information on our website is not, and shall not be deemed to be, a part of this Annual Report on Form 10-K or incorporated into any of our other filings with the SEC.
The text of this filing, as the company filed it with the SEC, without its images or exhibits. This is not investment advice.