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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 5 – <strong>Rare</strong> <strong>Earth</strong> Element Recovery/Alternative Material Use<br />

5.2.1 Collection<br />

The first step, defined as collection, is discussed in the recent report by UNEP (Schluep et al., 2009) and<br />

can be accomplished through a variety <strong>of</strong> means, but it is generally more efficient when a collection<br />

infrastructure is already established. In the past, state regulations have been effective at establishing the<br />

collection and recycling infrastructure required to increase recycling rates for consumer goods in the<br />

United States. For example, in the 1980s, the recycling <strong>of</strong> lead-acid car batteries became required by<br />

many states and resulted in a 95 percent recycling rate by 1990. The EPA data show that, nationally, 19%<br />

<strong>of</strong> consumer electronics were recycled in 2009 (Bomgardner, 2011). As <strong>of</strong> May 2011, 25 states have laws<br />

requiring e-waste recycling, and 5 additional states have pending laws. In most cases, manufactures are<br />

required to cover the costs associated with the collection and recycling. A summary <strong>of</strong> these state laws<br />

and information on collection volumes to date is available on the Internet (Electronic Take Back<br />

Coalition, 2011). In further support <strong>of</strong> electronics recycling, the Responsible Electronics Recycling Act<br />

was introduced into the U.S. House <strong>of</strong> Representatives in June 2011(H.R. 2284) and includes as one <strong>of</strong><br />

three main focus areas: support for collection, logistics, and supply chain optimization to support REE<br />

recycling.<br />

The EPA’s Plug-In To eCycling Partners website provides links to take-back programs and drop-<strong>of</strong>f<br />

locations for mobile devices, computers, printers, and televisions. The partners include retail stores,<br />

equipment manufacturers, and mobile device service providers. Together, they collected and recycled 68<br />

million pounds <strong>of</strong> used consumer electronics in 2008 (U.S. EPA, 2008b). Collection methods include<br />

direct mail <strong>of</strong> products to locations established by equipment manufactures and drop <strong>of</strong>f <strong>of</strong> used products<br />

at designated locations, such as retail stores or locations specifically setup as part <strong>of</strong> collection day events.<br />

Environmental impacts from the collection step are most predominantly due to transportation/shipping <strong>of</strong><br />

materials to the collection point and from the point <strong>of</strong> collection to the location <strong>of</strong> the processing facility.<br />

5.2.2 Dismantling/Preprocessing<br />

Dismantling and preprocessing steps are critical for separating the high-value components from less<br />

valuable materials. Frequently, high-value materials such as REEs and other metals, like gold, make up a<br />

small percentage <strong>of</strong> the item being recycled, and separation steps will make it more efficient to recover<br />

them. However, even when metals are separated from other nonmetal components, mixed metal scrap is<br />

more challenging to recycle than segregated metals.<br />

Typical dismantling and preprocessing steps include manual or mechanical separations, manual or<br />

mechanical disassembly, mechanical shredding, and screening. The specific details <strong>of</strong> each step are<br />

reported in the literature and are dependent on the item being recycled and the material being recovered<br />

(Schluep et al., 2009). Figure 5-2 provides photos <strong>of</strong> a facility where computer hard disk drives are<br />

manually disassembled, and <strong>of</strong> the resulting separated components, including magnets containing REEs.<br />

5-5

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