Source:
p. 5
Summary:
The deposit type of the Sevier Playa is a terminal lakebed (playa) brine deposit. The brine deposit is sedimentary in origin and composed of the natural concentration of mineral salts in groundwater found in the Playa. The brine is contained within the unconsolidated Playa sediments, composed primarily of clay and marl, a lime or calcium-rich clay. While the sediments may play a role in the mineral occurrence, development efforts to date have focused primarily on the mineral content found in the brine. The extractability of the brine Mineral Resource and the interaction between the brine mineralization and the potential for recharge by water flowing through the Playa sediments is part of this investigation, and an integral part of the determination of total extractable Mineral Reserves of SOP and other potential mineral compounds.
Composition of the thin salt crust covering the Playa consists of evaporite minerals and is approximately 3 to 4 inches (7.6 to 10.2 centimeters) thick, ranging up to as much as 18 inches (45.7 centimeters) in areas, as determined from drilling and augering data. Evaporite minerals forming the crust tend to be zoned on the Playa surface with halite (NaCl) being the dominant mineral in the center of the Playa, followed by glauberite (Na2Ca(SO4)2), and then gypsum (CaSO4) near the Playa shore (Godbe, 1984; Rasmussen, 1997).
Soluble salts, in the sediment-hosted brine, are the target mineralization of current development work. The source of soluble salts is the erosion and leaching of Paleozoic-era bedrock in the Sevier and Bear River drainages. Observation and sampling of Playa sediments and brine have identified the following features that characterize the top 100 feet (30.5 meters) of the deposit:
- Salt crust approximately 3 to 4 inches (7.6 to 10.2 centimeters) thick.
- Lateral zonation in crust mineral chemistry.
- Vertical zonation in sediment mineral chemistry.
- Variation in brine saturation both laterally and with depth.
- Variation in sediment grain size distribution.
- Artesian brine flow in some areas.
- Elevated concentrations of sodium, potassium, magnesium, calcium, chloride, and sulfate in the brine.
These features influence, to varying degrees, the target brine extent (volume) and potential for production of potash, halite, and bitterns from the brine. The focus of the Mineral Resource and Reserve estimates presented in this report are three shallow (depths less than 100 feet [30.5 meters]) brine saturated horizons termed the FCZ, MCZ and SCZ, from top to bottom. Below these horizons is a dry, hard clay.
Fat Clay Zone
The FCZ derives its name from its physical properties, being described predominately as plastic (fat) clay with low hydraulic conductivity. This dense gray clay is capped by a thin salt crust that is typically several inches thick over most of the Playa, but can range up to 18 inches (0.5 meters) thick in certain areas, according to CPMC auger logs(Gwynn, 2006). The FCZ averages approximately 12.8 feet (3.8 meters) in thickness and is comprised of two sub-horizons. The upper part of the FCZ consists of 9.35 feet (2.9 meters) thick homogenous, dense, plastic clay. This clay zone is observed to contain gypsum crystals up to 6- inches (15.2- centimeters) in diameter. Underlying this homogenous clay is a plastic clay zone, 1.64 feet (0.5 meters) thick that contains abundant organic material, commonly appearing as grass mats and root structures, representing a dry period when the Playa surface was covered by grassy beds. This organic clay zone is an important marker bed that separates the FCZ from the underlying MCZ below.
Marl Clay Zone
The MCZ is described as a gray, bedded, granular clay averaging 16.67 feet (5.1 meters) in thickness. The granular texture arises from what is observed to be silt-size granules of smaller clay particles loosely bound by a soft calcareous or gypsiferous matrix. The clay zone is also observed to contain numerous gypsum crystals up to 6-inches (15.2-entimeters) in diameter. An unconsolidated sand and gravel bed frequently occurs near the top of the MCZ, but is not consistent throughout the Playa. Where present, this sandy or gravelly zone averages a thickness of 18 inches (45.7 centimeters).
A dense zone of stiff clay averaging approximately 3.3 feet (1 meter) thick occurs approximately 2.9 feet (0.9 meters) below the sand and gravel bed, where present. It has been identified, in those exploration holes where handheld penetrometer readings have been taken, at regular intervals, in the core samples and used as a rough guide to determine the overall hardness of the Playa sediments. Penetrometer readings for the stiff clay zone of the MCZ range from between 1.5 to 3.0 st/ft2 (1.5 to 3 kg/cm2). For comparison, the surrounding marl clay has penetrometer readings between 0 to 1.25 st/ft2 (0 to 1.25 kg/cm2) The overlying fat clay has penetrometer readings between 0 and 0.5 st/ft2 (0.5 kg/cm2), and underlying siliceous clay has penetrometer readings ranging from 0.75 to 1.25 st/ft2 (0.75 to 1.25 kg/cm2).
Below the stiff clay bed is a further 9.8 feet (3 meters) of marl clay that transitions rapidly into predominantly siliceous clay, the underlying SCZ. The contact between the marl clay and underlying siliceous clay is easily supported by the sediment mineralogy and carbonate content test results from XRD mineralogy analyses. The average carbonate contents derived from drill core samples are illustrated in the stratigraphic column.
Siliceous Clay Zone
The SCZ is identified as an olive gray, quartz- rich clay with a relatively low carbonate content, averaging approximately 30% carbonates noticeably lower than the overlying MCZ. Four sand and gravel beds have been identified within the SCZ from drillhole records, but are not consistent throughout the Playa. The thickness of these sand and gravel units decreases from the margins of the lakebed toward the center of the Playa, where these beds are often missing from the drillhole records. Average thicknesses of the sand and gravel beds, where present, vary from 1.6 to 2.9 feet (0.5 to 0.9 meters). The base of the siliceous clay unit is marked by the presence of a dull red, dry, hard clay with hand-held penetrometer readings exceeding 5 st/ft2 (5 kg/cm2).
Drilling to date is insufficient to accurately determine a brine Mineral Resource potential below these three shallow aquifers.
Summary:
The proposed mining method for the collection of naturally- occurring brine from the sedimentary basin of the Sevier Playa involves a combination of stepped extraction trenches and drilled wells to collect the subsurface brine. The brine is conveyed into a series of solar evaporation and concentration ponds located on the surface of the Playa. The larger pre-concentration ponds are located in the northeastern portion of the Sevier Playa with the production ponds located in the southern portion of the Sevier Playa, with adjacent TMAs. Refer to the sections that follow for discussions on mine layout, extraction methodology, and construction methods, as well as supporting infrastructure.
In general, the mine design consists of the following four major components:
- Brine extraction system consisting of canals, trenches and wells
- Recharge system consisting of canals, collectors and trenches
- Series of evaporation ponds
- TMA.
The extraction and recharge trenches are placed throughout the Playa and their spacing and direction varies depending on permeability, conductivity, and/or concentration of the brine. The Playa is divided into mining units, referred to as BMUs. There are 21 BMUs; BMU1 to BMU11, and BMU13 to BMU22. Each BMU unit consists of extraction trenches, recharge trenches, recharge collectors, and extraction wells.
The extraction trenches within each BMU are connected to the extraction canal to facilitate direct flow. There are provisions in place to enable the operator to shut down the brine flow from a BMU to the extraction canal during operational shut-in phases. The brine flow from the extraction trenches is shut down by creating a blockage/plug at or near the point where the extraction trench feeds into the extraction canal. This blockage/plug is created by an excavator or dozer placing adjacent berm or spoil material from the trench excavation into the extraction trench. Sufficient material is placed so as to prevent brine flowing from the extraction trench into the extraction canal.
The recharge system consists of a diversion structure from the Sevier River to a distribution point. The distribution point directs the flow into both east and west recharge canals. The recharge water is introduced to each BMU through a series of recharge trenches and recharge collectors. The BMUs on the west side of the main extraction canal are recharged from the west recharge canal. Likewise, the BMUs on the east side of the extraction canal are recharged from the east recharge canal. Flows from the recharge canals to the recharge collector trenches of each BMU are controlled by valves in the side of the recharge canal.
Evaporation ponds are designed to contain the produced brine for the solar evaporation process. The berm embankments are designed to capture the precipitated salts in each of the pond systems. For the preconcentration ponds in the north, the salts are stored in place and the berms rise over time. These periodic raises match the deposition of the salts. In the south, production ponds remain at their initial elevation for the LoM considering that the precipitate products are collected and trucked to the Processing Plant for beneficiation.
Tailings are stored in three main areas. Type 1 tailings develop as precipitation occurs through the evaporation process. Type 1 tailings are generally halite and stored in the pre- concentration ponds located in the north of the Playa. A bitterns brine stream makes up the Type 2 tailings and they are stored in a sealed berm area in the southwestern portion of the Playa. Type 3 tailings, or Processing Plant flotation stream tailings, are managed in an on-site TMA through direct placement within a sealed berm.
The extraction trench system includes a central extraction brine canal that is fed by lateral extraction trenches. Extraction trenches collect and discharge brine into the extraction canal, which conveys brine to a bargemount pump lift-station located in a sump at the north end of the extraction canal adjacent to the preconcentration ponds. The extraction canal is sloped from south to north to allow for gravity drainage. The dimensions of the canal allow for both flow of the brine solution and minor sedimentation over the life of the Project. To the south, the canal is slightly smaller as the collected flows are not as great, and it is larger to the north to allow for increasing capacity.
Processing
- Granulation
- Flotation
- Dissolving & Crystallising
- Solar evaporation
Flow Sheet:
Summary:
The Processing Plant is designed to process potassium-bearing minerals recovered from harvesting ponds in order to generate SOP. The following design parameters were based on the usage of 68,760,097 short tons per year (STPY) (62,378,128.6 metric tonnes per year [MTPY]) of Playa brine feed to the Project.
The main source of process potassium losses are the ponds; as leakage, entrainment in pre- concentration ponds, and as purge brine losses. A small portion of the potassium ends up not being crystallized, and exits with the purge brine. The other source of losses for the process is in flotation, since even with high product recovery, some potassium will report to the flotation tailings. The remaining unit operations of the process are very efficient with recycle streams to minimize product losses as much as possible.
The process is designed to generate SOP from the evaporation and further treatment of Playa brine.
Saline brine from the Playa is extrac ........

Recoveries & Grades:
Commodity | Parameter | Avg. LOM |
Sulfate of potash (SOP)
|
Recovery Rate, %
| ......  |
Sulfate of potash (SOP)
|
Head Grade, %
| 5.28 |
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Projected Production:
Commodity | Units | Avg. Annual | LOM |
Sulfate of potash (SOP)
|
kt
| 338 | 9,243 |
Operational Metrics:
Metrics | |
Annual mining capacity
| ......  |
Annual production capacity
| ......  |
* According to 2018 study.
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Reserves at January 11, 2018:
Category | Tonnage | Commodity | Grade | Contained Metal | Recoverable Metal |
Proven
|
kt
|
Sulfate of potash (SOP)
|
|
1,049 kt
|
837 kt
|
Proven
|
kt
|
Potassium
|
3008 mg/L
|
471 kt
|
|
Probable
|
kt
|
Sulfate of potash (SOP)
|
|
6,685 kt
|
5,334 kt
|
Probable
|
kt
|
Potassium
|
1585 mg/L
|
3,000 kt
|
|
Proven & Probable
|
kt
|
Sulfate of potash (SOP)
|
|
7,734 kt
|
6,171 kt
|
Proven & Probable
|
kt
|
Potassium
|
|
3.471 kt
|
|
Measured & Indicated
|
kt
|
Sulfate of potash (SOP)
|
|
26,821 kt
|
|
Measured & Indicated
|
kt
|
Potassium
|
|
12,036 kt
|
|
Inferred
|
kt
|
Sulfate of potash (SOP)
|
|
1,642 kt
|
|
Inferred
|
kt
|
Potassium
|
|
737 kt
|
|
Corporate Filings & Presentations:
Document | Year |
...................................
|
2020
|
...................................
|
2019
|
...................................
|
2018
|
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