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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 3 – Life-Cycle Stages <strong>of</strong> <strong>Rare</strong> <strong>Earth</strong> <strong>Elements</strong> Mines<br />

3. Life-Cycle Stages <strong>of</strong> <strong>Rare</strong> <strong>Earth</strong> Mineral Mines<br />

The increasing importance <strong>of</strong> REMs for the manufacture <strong>of</strong> modern devices upon which society has become<br />

reliant, along with uncertain supplies (see Section 2), is encouraging exploration and development <strong>of</strong> new mining<br />

sites. While REMs are an important resource needed to sustain our modern technologies, the waste footprint and<br />

environmental impact from REM mining operations is expected to be as significant as current mining practices for<br />

metals and minerals. The requirements, regulations, and financial obligations and assurances for a new mine are<br />

usually complex and take years <strong>of</strong> planning. The economic feasibility <strong>of</strong> discovered deposits must be proved, and<br />

environmental effects to the local communities and habitat also must be evaluated to determine feasibility. The<br />

process <strong>of</strong> exploration, development, and construction typically required before mining can begin may exceed 10<br />

years. Except for a few locations, known rare earth deposits in the United States are generally considered small<br />

to medium reserves. This section presents a discussion <strong>of</strong> the typical process steps used in developing a new<br />

rare earth deposit and the associated mining wastes that typically would result. It is not expected that the mining<br />

stages <strong>of</strong> a rare earth mine would be different than other hardrock or metal mining operations. Except for the<br />

radioactivity <strong>of</strong> uranium and thorium, the potential REM waste emissions would be generally comparable to a<br />

typical hardrock mine.<br />

Mining operations produce a variety <strong>of</strong> solid materials that have the potential to cause environmental<br />

contamination and require long-term remedial actions and operation and maintenance. The largest mines<br />

may generate more than a billion tons <strong>of</strong> solid wastes that may cover areas exceeding a thousand acres,<br />

and smaller operations still must handle and dispose <strong>of</strong><br />

quantities <strong>of</strong> materials that can affect large areas (U.S.<br />

EPA, 2003). Most deposits <strong>of</strong> REE ores in the United<br />

States would be expected to require mining operations<br />

that likely would produce far less quantities <strong>of</strong> solid<br />

wastes than the largest operating mines. An example<br />

<strong>of</strong> an existing REE mine in the United States that<br />

would be considered a large mining operation, is the<br />

Molycorp Minerals rare earth mine in Mountain Pass,<br />

California (see sidebar). It would be expected that rare<br />

earth mineral mining operations developed in the<br />

United States would be similar to other large hardrock<br />

and placer mines that recover minerals containing<br />

primary metals (e.g., gold, silver, copper, zinc, lead).<br />

As examples, the mass <strong>of</strong> selected types <strong>of</strong> individual<br />

REE-containing ore deposits occurring in the United<br />

States is estimated by the USGS to be the following:<br />

� 0.2 million tons (approximate average) for<br />

thorium-rare earth vein deposits<br />

(Armbrustmacher et al., 1995)<br />

� 3.5 to 450 million tons for low titanium iron<br />

oxide deposits containing REE, with a median<br />

quantity <strong>of</strong> 40 million tons (Foose, 1995)<br />

� 6.6 to 331 million tons for minable carbonatite<br />

ore deposits (Modreski et al., 1995).<br />

These rough quantity estimates are based on known<br />

deposits, as characterized in geochemical deposit<br />

models prepared by the USGS; other deposit models<br />

may also exist other than those found and reviewed<br />

and that provide additional estimates. Averages for the<br />

3-1<br />

The Scale <strong>of</strong> an Existing REE Mine<br />

in the United States<br />

The largest rare earth minerals mine in the<br />

United States is Molycorp Mineral’s Mountain<br />

Pass rare earth mine and site, which occupies<br />

2,222 acres <strong>of</strong> land in San Bernardino County,<br />

California. The mine started operation in 1952,<br />

operating as an open pit lanthanide mining,<br />

beneficiation, and processing facility. The period<br />

<strong>of</strong> greatest ore production was from 1965 to 1995.<br />

Mining activities ceased in 2002, but minor milling<br />

activity continued to process stockpiled ore; and<br />

full-scale ore production may resume in 2012.<br />

When mining activities ceased, the open pit was<br />

1,500-feet wide by 400-feet deep. Overburden<br />

materials were held on site, and numerous<br />

process water, tailings, and product storage ponds<br />

were also operated.<br />

Remaining REE reserves (relative to a 5<br />

percent cut<strong>of</strong>f grade) at the Mountain Pass mine<br />

are estimated to exceed 20 million tons. The<br />

average REE content in the bastnasite mineral ore<br />

is approximately 9 percent. The remaining gangue<br />

minerals (calcite, barite, and dolomite) in the<br />

carbonatite igneous rock body make up<br />

approximately 91 percent <strong>of</strong> the ore-containing<br />

rock. The expected overburden produced is<br />

estimated to be 104 million tons, which will be<br />

stored at two existing storage piles. These storage<br />

piles will together cover approximately 315 acres<br />

within 30 years <strong>of</strong> the proposed period <strong>of</strong><br />

operation through 2042 and represent<br />

approximately a 120 percent change over current<br />

stockpiles accumulated between 1950 and 2002.<br />

California Regional Water Quality Control<br />

Board, Lahontan Region (2010)

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