03/12/2026
BRPA's response to the Sheep Creek Mine Plan of Operation:
Dear Ranger Pliley,
The Bitterroot River Protection Association (BRPA) wants to thank you for allowing comment on the record concerning the Draft Plan of Operation for the Sheep Creek Project USFS Submittal Exploration and Bulk Sampling which was submitted by US Critical Materials to do exploratory mining in the headwaters of the West Fork of the Bitterroot River. We realize that you are only in the initial stages of the process and that the plan may change, perhaps substantially, prior to being deemed complete and triggering a public review process under NEPA which will allow a limited period for official public comment. However, this Draft Plan is so glaringly deficient in providing even the most basic information required for proper review we believe that submitting comments at this time may be of some help to the Forest Service in arriving at a Final Plan of Operation that has enough information that your agency and the public can make an informed decision about the proposal.
BRPA was formed over a quarter of a century ago with the general aim of preserving and protecting the Bitterroot River watershed. As part of that effort in 2017 we instituted the Bitterroot River Health Check program a citizen science based cooperative headquartered at the Bitterroot College UM. In cooperation with Montana DEQ, the Bitterroot National Forest, the UM Watershed Health Clinic, the Montana Watershed Coordination Council, Montana Trout Unlimited Bitterroot Chapter, the Clark Fork Coalition, Bitterrooters for Planning, Friends of the Bitterroot, the Ravalli County Fish and Wildlife Association, BRPA has led a team of two dozen volunteers annually in water quality monitoring across the Bitterroot River watershed establishing seven permanent monitoring stations on the mainstem of the river and on 15 tributaries over the last eight years. We have an intense interest in protecting and preserving the water quality and quantity in the entire Bitterroot River watershed and are very concerned about the potential negative impacts that a Rare Earth Element mine in the headwaters of the West Fork present to the river and to the entire community. Potential negative impacts of this proposed mine on water quality and quantity in the watershed are enormous and deserve a good hard look.
BASELINE MONITORING
In our discussions with the Bitterroot National Forest Supervisor during the scoping meetings for the Bitterroot Front Project it was agreed, based on consultation with the Forest service hydrologist at the time, the elementary basics of any large ground disturbing activity on the forest required establishing a baseline for the environmental conditions, especially the water, prior to any ground disturbing activity; continued monitoring during the project activity and follow-up monitoring following completion of the project. We presume that these simple and undisputed requirements apply to the proposed REE mine in the headwaters of the West Fork.
We would expect that the baseline monitoring appropriate for this project in terms of the water alone would include at a minimum:
• _Baseline information on potentially impacted water resources, including local geology and hydrology;
• _Baseline characteristics of potentially impacted surface waters, groundwater, seeps and springs;
• _Geotechnical information related to potential dewatering impacts related to exploration activities;
• _Assessment of the quantity and quality of groundwater that is likely to be produced by mining or exploration activities;
• _Information on planned consumptive (or non-consumptive) water use;
• _Information on water rights owned or required for water use from local surface or groundwaters;
• _Baseline water quality data (nutrients, sediments, metals, REEs, etc…), including applicable water quality standards and how those standards will be met;
• _Baseline information on water temperature and how existing temperatures will be maintained;
• _A plan for stormwater management both as a result of exploration and/or onsite waste rock storage;
• _Baseline information on potentially impacted aquatic life, fisheries (populations and habitat), and/or sensitive or protected species such as ESA-listed bull trout and native Westslope cutthroat trout; and macro-invertebrates.
• _Information related to the potential direct or incidental discharge of pollutants to groundwater or surface waters or the required discharge permits;
• _Information necessary to assess the feasibility of the suggested “zero discharge” processing system, including what processing steps will be conducted on site, what water treatment steps will be required to re-use process water, and any plan for the disposal of solids or other contaminants removed from process;
• _Any plan for wastewater treatment and discharge if excess groundwater or process water requires disposal; or
• _Information related to water monitoring efforts required to ensure compliance with applicable standards and evaluate ongoing impacts to water quantity and quality.
Especially significant is the need to do preliminary testing for the presence of asbestos due to the presence of fibrous actinolite. The Forest Service must require site-specific asbestos characterization, fiber-release potential analyses, and enforceable exposure controls before authorizing any activities that could disturb actinolite-bearing formations.
WASTE ROCK
Although the company told the public and the County Commissioners just two weeks before submitting this plan that no chemicals would be used in the process, the plan actually includes a large amount of explosives and fuel to be stored on the site.
Mine exploration and excavation, particularly using conventional explosives, often result in significant environmental contamination, leaking toxins like TNT, RDX, heavy metals, nitrates and ammonia, into soil and groundwater.
It appears that the Plan involves leaving a large quantity of its muck and waste rock in the mine shafts (drifts and vaults) and entrance ways (portals).
“Waste rock or blasted rock that does not contain recoverable minerals will be utilized as internal fill within the adit to fill voids and further production. Any waste material that is produced that cannot be utilized as internal fill will be used to build up the portal pad locations shown on the site map.” (pg. 12 of Plan)
“Muckers are used to transport blasted rock and materials underground for removal to the surface or for placement of waste rock into areas of the site as part of the exploration process.” (pg. 19 of Plan)
A number of mining methods are discussed-
In discussion of the resue method it is mentioned that “Once the drift has been driven (advanced) to the desired length, the waste contained in the back (roof) will be selectively blasted and left in place to provide the base for the next “lift” or level of the section of ore body. This allows the ore vein to be selectively removed while using the blasted waste rock as a road base for sequential sampling.” (pg. 26 of the Plan)
In discussion of the Long Hole Extraction method it is mentioned that “This is still considered a selective exploration method where the focus is on taking the ore and waste separately to improve ore grade. This method requires an excavation shape similar to the resue method, however instead of extracting one level upon the next, the levels are separated by a pre-determined distance.” “This ore is then blasted and retrieved via a remote mucker pictured at the bottom center of the image. Once the ore has been removed, waste can then be hauled back in to fill the void left by the removal of the ore…” (pg 27 of the Plan)
In discussion of the Overhand Ramp and Fill Method it is mentioned that “This method is similar to Resue and in that it relies on the placement of waste rock back into the excavated heading to continue the extraction sequence. A drift (tunnel) is driven on the ore body shown here on the bottom of the image. In this bottom image, the first drive has taken place, and waste has been placed back into that void to allow for the exploration of subsequent levels or lifts. As seen in the upper portion of the image, this process is repeated until the angle of the attack ramp becomes too steep to safely navigate. This allows for multiple cuts (lifts or levels) to take place from a single access point. (pg. 28 of the Plan).
Although the plan’s methods call for separating and removing the “highest grade material” separate from the waste it is unreasonable to suppose that the waste will not contain low to medium grades of the target material as well as significant amounts of explosive residue including TNT, RDX, heavy metals, nitrates and ammonia.
Because waste rock and low/medium grade ore produced in this process is being produced from an area with sulfide mineralization, geochemical testing of each rock type that will be encountered is necessary to determine the likelihood that dissolved metals could be produced when the waste rock/sub-grade ore is exposed to air and water. However, no geochemical characterization data was provided in the Plan. [see attached letter from David Chambers at the Center of Science in Public Participation]
In addition to checking the waste material for concentration levels of mercury, selenium, lead and other heavy metals, it also needs to be tested for concentration levels of rare earth elements. This information is necessary in determining the health risks associated with the waste rock.
The company states, “The deposits are also unique due to low levels of thorium, which potentially allows for mining with minimal environmental impact. The levels of thorium averaged 200ppm, which is significantly below the 500-ppm permitting threshold established by the Nuclear Regulatory Commission, a U.S. government agency.”
It is not clear how they arrived at this average estimation. Since the Plan calls for separating the highest grade ore from lower grade ore and waste rock clarification is needed. Is it the high grade ore alone that averages 200 ppm? Or was that average based on the total amount of waste rock and lower grade ore as well? If it’s the latter, then the high grade ore that is being stored separately and shipped separately could have a significantly higher average amount of Thorium and in fact trigger the involvement of the Nuclear Regulatory Agency.
Regardless of the answer to that question, the real question is not whether that agency will be involved due to the level of Thorium. The real question is the level of health risks associated with the materials as a whole including waste rock, low and medium grade ore, being stored in the mine, on site or used elsewhere; as well as the high grade ore being transported to the lab.
The state of Montana and the U. S. Forest Service could benefit greatly, we believe, in looking at what other countries in the world can offer in terms of providing adequate protection for human health and the environment posed by the extraction of Rare Earth Elements.
EURA, a project funded by the European Commission for the 'Development of a sustainable exploitation scheme for Europe's Rare Earth ore deposits' has published an internal guidance report on “Health and safety issues in REE mining and processing” intended for internal guidance within the EURARE project on health and safety issues in the mining and processing of REE ores.
This involved developing methods in all parts of the production chain, i.e. exploration, mining, ore beneficiation, extraction of REEs from ore concentrates, isolation of the individual REEs and the production of REE metals and alloys. The report describes on a country-by-country basis how “REE mining and production have led to some significant environmental and health impacts.” In Brazil, China, India, Malasia and the United States.
According EURA’s health and safety issue report, it should act both as a project baseline and as a guide to ensure the health and safety of all people involved.
Due to the radionuclide content of some of the EURARE ores, consisting of natural uranium and/or thorium and their decay chains, the report addresses radiation protection issues.
On page six in introductory remarks they note that “The rare earth elements (REE) are a group of metals comprised of yttrium (Y), the fourteen lanthanide elements, i.e. lanthanum (La), cerium (Ce), praseodymium (Pr), neodymium (Nd), promethium (Pm), samarium (Sm), europium (Eu), gadolinium (Gd), terbium(Tb), dysprosium (Dy), holmium (Ho), erbium (Er), thulium (Tm), ytterbium (Yb), and lutetium (Lu), and sometimes scandium (Sc).”
The Sheep Creek Mine deposit contains many of these REEs some of them specifically referenced as targets by US Critical Materials. In a press release (Newswires July 27, 2022) the company noted that “The key property elements include neodymium and praseodymium. The project also includes cerium, dysprosium, europium, gadolinium, lanthanum, niobium, scandium, strontium, samarium, and gallium.”
If US Critical Materials and the Bitterroot National Forest intend to mine REEs in the headwaters of the Bitterroot River it is imperative that they conduct an Environmental Risk Assessment.
Environmental Risk Assessment (ERA) examines processes, emissions, the spread of contaminants and exposures to humans and biota. ERA is a systematic procedure for predicting potential risks to human health or the environment. A complete ERA process includes both ecological and human health risk assessments and the preceding assessment of hazards and the related exposure concentrations. A model for this type of assessment has been developed.
The MINERA project (Improving environmental risk assessments for metal mines) was carried out in collaboration between the Geological Survey of Finland (GTK), the National Institute for Health and Welfare (THL) and the University of Eastern Finland (UEF) during 2010–2013. The Minera-project developed the general model for environmental risk assessment for a metal mine site. The Minera-model consists of both, ecological and health risk assessments that are preceded by an examination of the mining processes, emissions, the transport of contaminants and the resulting concentrations in the surrounding media (Kauppila et al. 2013, Figure 2-1).
https://www.eurare.org/docs/internalGuidanceReport.pdf?ref=hir.harvard.edu
There is an international radioactive waste classification scheme and a safety guide defining six levels of risk ranging from Exempt waste to High Level waste. What level of waste is expected from the Sheep Creek Mine?
There are occupational health and safety issues with rare earths (Rim et al. 2013). What is US Critical Materials’ plan for protecting workers? Is the proposed ventilation system adequate with respect to all the elements involved?
Elevated concentrations of REEs may also cause toxic reactions and negative effect on plants (Tyler 2004). How is dust, which may impact surrounding soils and vegetation being controlled at the adit pads and at the loading site near the bottom of Sheep Creek where ore and mine waste will be stored prior to loading for off-site transportation?
It is necessary to determine the concentration levels for all the individual metals and REEs in the deposit to make any reasonable determination of the health risks involved at every stage of this project; as well as a detailed plan for handling them throughout the process from tunneling, to extraction, and to delivery either to the lab or to undisclosed construction sites or off-site storage areas.
WATER
The huge amount of fractured waste rock and muck that is proposed to be stored indefinitely within the mine, combined with the predicted groundwater inflow presents a very significant potential for contamination of groundwater in the area. The likelihood that dissolved metals could be produced is dramatically increased when the waste rock is exposed to air and water.
The Plan assumes that there will be groundwater inflow and aims to use it to fill a 15,000 gallon holding tank for use in the mining process. The Plan states that the mining exploration will operate on a zero-discharge basis by recycling and “clarifying” the water contained in the reservoir. Once the reservoir is full it seems that the initial inflow would have to cease or be diverted. To divert it without a provisional MPDES permit any discharge would automatically be a violation of Montana water quality regulations. It should be acknowledged in the Plan that a situation where more water than could be utilized and/or temporarily stored could be encountered, and a contingency plan for treating and discharging excess water discussed.
The Plan suggests that the excess inflow would be addressed by grouting the area to stop the leakage. This is a dubious solution in a tunnel system over a mile long with dozens of side vaults. It is unreasonable to depend on grouting to stop the inflow of water into the mine workings. If by some miracle they would be able to stop it they would then have to account for how they would replenish the holding reservoir as some loss of water in the mining process is inevitable.
Seepage and drainage collection must be carefully planned, and the chemical nature of the water that comes into contact with the waste rock must be characterized. Waste rock taken adjacent to the ore zone will contain virtually all of the metal contaminants contained in the ore, but not enough of the target metal to justify processing as ore. Waste rock produced from driving access tunnels away from the ore zone must still be tested to determine whether any sulfide minerals are present, even though this rock is not directly adjacent to the ore.
The Plan does not contain any information about the total quantity of water that will be required for the proposed mining operation and associated road construction and other dust abatement activities.
The only estimation of water use is the 15,000 gallons of groundwater inflow that will be captured for a closed-loop recycling operation for the mining process and no provision for treating excess water once the holding reservoir is filled has been proposed except for grouting any leaks which is a dubious remedy in a combined length of over a mile of tunnels including dozens of side vaults.
There is no discussion about the inevitable loss of some water during the mining process or the amount required for dust abatement in the new road construction and use which will also be lost. That they anticipate the need for more water than what the reservoir can hold is plainly stated in the Plan: “If additional process water is required, a source such as Sheep Creek, or the West Fork of the Bitterroot River to supplement activities underground would be needed.” (pg. 13 of the Plan)
There is no indication whether they have the right to take it from Sheep Creek or the West Fork of the river in a basin that is closed to any further surface water rights. Neither do they discuss the potential impacts to downstream irrigators if they do somehow succeed in taking water out of Sheep Creek and the West Fork of the river.
The potential impacts on Painted Rocks Reservoir, the potential contamination to the water and soils behind the dam have not been examined. This reservoir supports irrigation and helps make the West Fork fishery a trout stronghold by adding cold water from the reservoir to the late season warmed river water. Pollution of Painted Rocks would be a big risk to existing locally owned, proven-sustainable, fishing industry as well as local irrigated agriculture. Milltown dam, east of Missoula, demonstrated the unfortunate role of acting as a tailings impoundment for both decades-long chronic mining-derived water pollution as well as a backup for catastrophic pollution when the Mike Horse mine tailings dam
failed. The values at risk at Painted Rocks deserve special consideration early in the planning process. The Agency must analyze the impacts the mine will have on all aspects of the Bitterroot River fisheries including economic values, water quality, impacts to agriculture, tourism, and habitat degradation and must further demonstrate compliance with all state and federal standards relating to these factors.
The Forest Service and the public need much more information to assess the feasibility of the suggested “zero discharge” processing system, including what processing steps that will be conducted on site, what water treatment steps will be required to re-use process water, and any plan for the disposal of solids or other contaminants accumulating in the holding tank and potentially removed from the process
Hydrological analysis and predictions of the amount of “contact” water that will be generated from the surface area required for the mine workings, temporary waste rock storage pad, permanent waste rock disposal, and whether any seepage might occur from the new underground workings, should be included in the proposed Plan. A contingency plan to treat excess water should be developed, and the funding required to execute this plan disclosed. The amount of water to be used in dust abatement in every aspect of the operation including the access roads should be disclosed.
Also related to water, the Plan contains insufficient information about estimated stormwater and any stormwater management system for the site. Stormwater forecasting, including 50- and 100-year precipitation (especially rain on snow) events should be included in the Plan, along with how the operation will manage regular and historic stormwater flows. The Plan should provide information on how stormwater may impact adjacent surface water quality and, hence, aquatic life for all seasons and life cycles.
ROADS
The “Roads Development” section of the Plan references clearing and improving both existing USFS roads (5685), as well as historic mining access roads that are, to our knowledge, little more than closed, regenerating road prisms. Any work on historic roads that are not part of the current, maintained Forest road system should have to undergo environmental evaluation as new roads. Regardless of whether it is the improvement or maintenance of old roads or existing FS roads, such as 5685, USCM must provide far more detailed information about the extent of road widening and clearing it deems likely for mine exploration over the full life of the exploration operations.
WILDLIFE AND WILDLIFE HABITAT
This proposed activity in the Sheep Creek Drainage requires an Environmental Impact Statement under the National Environmental Policy Act (NEPA) not only for the potential impacts on water but also on wildlife and wildlife habitat across the watershed. The area supports critical habitat for several species of concern, including Westslope Cutthroat Trout (the Westfork is a stronghold for native Westslope Cutthroat Trout) and bull trout, which is listed under the Endangered Species Act. A couple of macro-invertebrate species also listed as species of concern, the Rocky Mountain Tailed Frog and the Northern Rocky Mountains Refugium Caddisfly have been identified within the mining claim areas.
Many miles of the roads referenced in the Plan are adjacent to the West Fork Bitterroot, Sheep Creek and other tributaries. Thus the potential impacts to riparian habitat should be evaluated, both in terms of loss of riparian cover and potential for sediment transport into any surface water source near roads. Loss of riparian cover or addition of sediment to streams, like the water quality and quantity impacts discussed above, risk negative impacts to aquatic life, fish, and macroinvertebrates.
Other species such as grizzly bears, wolverines, and Canada lynx also roam in or near the proposed mine area, and the project would fragment these identified wildlife corridors. Other species of conservation concern like rocky mountain sheep, elk, mountain goats, and Northern Rockies fisher also inhabit the area. Road construction, drill pads, and other infrastructure could degrade these habitats permanently. The value of this linkage corridor to biodiversity is vital to the survival and continued viability of these species.
LOCAL GOVERNMENT SERVICES AND THE ECONOMY
Potential impacts on local government services also need to be examined. The proposed mine will create impacts to the majority of locally provided services including, law enforcement , search and rescue, roads and bridges, wildland fire, volunteer fire department, educational and medical as well as air quality considerations. We believe that the local government, as the elected body representing the U. S. citizens who stand to be most immediately impacted by the proposed activities should have a seat at the table in any decisions made by the U. S. Forest Service regarding the Sheep Creek mine proposal.
Although the company estimates that it may have positive impacts on the economy in terms of a few jobs that may or may not be filled by local residents or existing businesses in the county, the potential negative impacts on the Bitterroot Valley economy as a whole are enormous. The Bitterroot Valley's economy is strongly tied to its natural landscape-from agriculture to recreation (fishing, tourism) to real estate and the large portion of unearned income related to the associated forest and wildland amenities, and any damage to water quality or wildlife and wildlife habitat could impose long-term costs on local businesses and livelihoods. A method and formulas exist to examine these potential impacts. (for example: https://stock.scholars.harvard.edu/sites/g/files/omnuum5911/files/stock/files/snf_withdrawal_ea_stock_and_bradt_aug6_2018.pdf
We strongly urge the agency to require an adequate assessment of these potential negative impacts prior approving any ground disturbing activity.
CULTURE
Pursuant to the Antiquities Act and in consultation with the Salish and Nez Perce tribes, a thorough archeological survey should be completed prior to any ground disturbing activities. We believe the tribes should be consulted concerning every aspect of the proposed activities on the forest.
The project also must comply with all Bitterroot National Forest Plan goals, objectives, and standards. In analyzing the project impacts, the Bitterroot National Forest must demonstrate compliance with all applicable goals, objectives and standards.
Thanks for your consideration of our comments,
Michael Howell
Executive Director
Bitterroot River Protection Association