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Rare Earth Elements: A Review of Production, Processing ...

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<strong>Rare</strong> <strong>Earth</strong> <strong>Elements</strong> <strong>Review</strong> Section 6 – Human Health and Environmental Risks<br />

radioactive materials found deeper in the soil column or accumulated sediments are generally shielded by<br />

the top layer <strong>of</strong> soil. Geometric attenuation generally limits the external radiation from naturally<br />

radioactive materials with no interposed shielding materials to within a few meters (i.e., less than 5 meters<br />

and <strong>of</strong>ten less than 1 to 2 meters from the source). Radioactivity can become concentrated in mineral<br />

scales that develop in groundwater recovery wells, holding tanks, aeration ponds, and milling processes<br />

areas. Inhalation <strong>of</strong> contaminated dusts is generally <strong>of</strong> greatest concern for naturally occurring radioactive<br />

materials.<br />

Tailings storage facilities typically receive the bulk <strong>of</strong> processing water, which is normally recycled, but<br />

some <strong>of</strong> it could be released into the environment through seepage or overflows due to unusually high<br />

rainfall. The tailings storage facilities (TSF), when dry, usually represent the main source <strong>of</strong><br />

radon/thorium and dust emissions to the environment. Special containment arrangements are required for<br />

the disposal <strong>of</strong> tailings generated during chemical and/or thermal processing <strong>of</strong> uranium and thoriumbearing<br />

minerals to ensure that environmentally mobile radionuclides are not released into the<br />

surrounding environment. The disposal <strong>of</strong> contaminated equipment and materials also needs to be<br />

controlled. In addition, the possibility <strong>of</strong> <strong>of</strong>f-site contamination from trucks and equipment moving <strong>of</strong>fsite<br />

needs to be considered.<br />

After milling and concentrating, the mineral is sometimes stockpiled at the mine site prior to transport to<br />

the processing sites, and these stockpiles may contain radioactive minerals in concentrations sufficient to<br />

produce elevated radiation levels and radon. The stockpiles, therefore, need to be protected against<br />

unauthorized access and also against the possibility <strong>of</strong> the material spreading through wind saltation.<br />

Ideally, stockpiles containing radionuclides in concentrations that require signposting <strong>of</strong> areas as<br />

“supervised” and/or “controlled” should be located on a concrete slab to simplify the management and<br />

clean-up operations.<br />

The tailings from the separation and downstream processing <strong>of</strong> minerals may contain radionuclides in<br />

concentrations that could give rise to unacceptable levels <strong>of</strong> radiation and radon. Appropriate<br />

management is typically required, and the disposal <strong>of</strong> the waste will depend on the method used to<br />

process the mineral and on the respective levels <strong>of</strong> radiation and the concentration <strong>of</strong> radon gas emitted.<br />

The possibility <strong>of</strong> ground water contamination increases if chemical and/or thermal treatment <strong>of</strong> the<br />

mineral occurs (e.g., in the case <strong>of</strong> separating the heavy mineral sands). Otherwise, the radionuclides in<br />

the tailings could be considered as remaining bound in the individual mineral grains; therefore, the<br />

possibility <strong>of</strong> the contamination <strong>of</strong> groundwater by radionuclides from tailings is not considered to be less<br />

significant. Radium may be present in the tailings water, which would require removal before being<br />

disposed.<br />

Where any grinding, chemical, and/or thermal treatment <strong>of</strong> minerals containing radionuclides takes place,<br />

additional safeguards must be implemented due to the fact that secular equilibrium in both uranium and<br />

thorium decay chains may be disrupted. This could result in an increased environmental mobility <strong>of</strong><br />

radionuclides, such as radium and radon. Cleaning <strong>of</strong> certain minerals prior to processing (such as, for<br />

example, the cleaning <strong>of</strong> the heavy mineral sand grains) may produce finely powdered waste (slimes).<br />

Slime wastes may have significant uranium or thorium content, and the disposal as radioactive waste may<br />

be required.<br />

The equipment used in downstream processing <strong>of</strong> minerals <strong>of</strong>ten becomes contaminated by NORM or<br />

TENORM. Contaminated equipment must either be disposed <strong>of</strong> properly, or thoroughly decontaminated<br />

prior to any re-use. Scales and sludge build on the inside surfaces <strong>of</strong> pipes and vessels used in chemical<br />

and thermal processing, and these materials <strong>of</strong>ten have elevated levels <strong>of</strong> radionuclides.<br />

6-9

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