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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 />

From a previous study (U.S. EPA, 1995) <strong>of</strong> risks to human health and the environment from hardrock<br />

mines, it was concluded that the 66 hardrock mining cases illustrated that significant human health and<br />

environmental damages were caused by the management <strong>of</strong> wastes from mining and mineral processing,<br />

particularly placement in land-based units. Molycorp Minerals rare earth mine in Mountain Pass, CA, was<br />

one <strong>of</strong> the sites included in the study. Wastes subject to the RCRA Bevill Amendment were found to be<br />

the cause <strong>of</strong> the damages. These damages occurred in all hardrock mining sectors and across all<br />

geographic regions <strong>of</strong> the United States. Table 6-2 excerpted from the report summarizes the type <strong>of</strong><br />

impacts.<br />

Table 6-2. Frequency <strong>of</strong> Various Types <strong>of</strong> Impacts from CERCLA Sites (U.S. EPA, 1995)<br />

Type <strong>of</strong> Impacts<br />

Portion <strong>of</strong> Damage Cases<br />

(Total NPL Sites = 66)<br />

Surface water contamination 70 percent <strong>of</strong> cases<br />

Ground water contamination 65 percent<br />

Soil contamination 50 percent<br />

Human health impacts 35 percent<br />

Flora and fauna damage 25 percent<br />

Air dispersion or fugitive emissions 20 percent<br />

6.1.2.2 Acid Mine Drainage at CERCLA Sites<br />

In another review by EPA <strong>of</strong> 156 hardrock mine sites, the results showed that approximately 30 percent<br />

(or about 45) <strong>of</strong> the sites had problems with acid mine drainage (U.S. EPA, 2004). The report also<br />

suggested that acid mine drainage occurred most <strong>of</strong>ten in EPA Regions 8, 9, and 10. The EPA OIG<br />

(2004) also reiterated the concern from the National Wildlife Federation that sites where AMD is present<br />

should be carefully monitored as “the presence <strong>of</strong> acid mine drainage is either underestimated or ignored<br />

until it becomes evident, at which time the costs <strong>of</strong>ten exceed the operator’s financial resources, leading<br />

to bankruptcy or abandonment <strong>of</strong> the site in many cases.” As previously stated, it is not anticipated that<br />

the mining <strong>of</strong> REE will typically produce AMD given the typical geochemistry <strong>of</strong> these deposits.<br />

6.1.2.3 Prospective REE Mining Sites and CERCLA <strong>Review</strong><br />

A comparison <strong>of</strong> USGS (Orris et al., 2002) data and EPA CERCLA documents revealed four mines that<br />

have been damage case sites. While these sites are not yet being mined for REEs, they have been<br />

identified as potential future sources:<br />

� Maybe Canyon Phosphate Mine (Superfund site);<br />

� Mountain Pass REE Mine (when owned by Molycorp; not to be confused with current owner,<br />

Molycorp Minerals, LLC);<br />

� Smoky Canyon Phosphate Mine (Superfund site); and<br />

� Bokan Mountain Uranium Mine (not on NPL but Federal Facilities review site).<br />

Releases <strong>of</strong> radionuclides were the environmental impacts that were investigated for both Mountain Pass<br />

and Bokan Mountain mines. Maybe Canyon Mine was in operation between 1977 and 1984.<br />

Approximately 120 acres <strong>of</strong> waste rock (29 million cubic yards) was present from which selenium and<br />

other hazardous substances were reported to have contaminated ground water and surface water (U.S.<br />

Department <strong>of</strong> Agriculture, 2011). Selenium contamination is a common problem at phosphate mines and<br />

it was also found to be an environmental contaminant <strong>of</strong> concern at the Smoky Canyon Mine.<br />

6-13

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