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SUbstance flow analysis of the recycling of small waste electrical ...

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4. Data inventory 75<br />

was applied to sort <strong>the</strong> WEEE out <strong>of</strong> <strong>the</strong> residual <strong>waste</strong> and feed this to a treatment facility<br />

for WEEE, so that <strong>the</strong> gold and palladium contained in sWEEE disposed <strong>of</strong> toge<strong>the</strong>r with<br />

residual <strong>waste</strong> are assumed to be discarded.<br />

4.1.3. Reuse<br />

Because reuse <strong>of</strong> EEE is covered by this investigation, “only” data on reuse <strong>of</strong> WEEE are<br />

needed. Defining a clear boundary between reuse <strong>of</strong> WEEE and reuse <strong>of</strong> EEE in practice is<br />

a challenge, as emphasized by Prelle (2008).<br />

Data on reuse <strong>of</strong> WEEE in Germany in 2007 under <strong>the</strong> responsibility <strong>of</strong> <strong>the</strong> manufacturers<br />

were published by BMU (2008), and this is summarized by Table 23.<br />

Table 23<br />

Quantity <strong>of</strong> WEEE reused under <strong>the</strong> responsibility <strong>of</strong> <strong>the</strong> manufacturers in Germany in<br />

2007 (tonnes)<br />

Category according to WEEE Directive Reused<br />

2- Small household appliances 662<br />

3- IT and telecommunications equipment 2705<br />

4- Consumer equipment 343<br />

6- Electrical and electronic tools 181<br />

7- Toys, leisure and sports equipment 25<br />

Little information is available about <strong>the</strong> reuse <strong>of</strong> sWEEE in Germany besides <strong>the</strong> data from<br />

BMU (2008). Greener Solutions (2008) reported that mobile phones <strong>the</strong>y collected in 2007<br />

were reused in Asia or Africa.<br />

The reuse rates depend not only on <strong>the</strong> collection channel, but also on <strong>the</strong> equipment types.<br />

It was assumed that <strong>the</strong> reuse rates are higher for sWEEE collected by <strong>the</strong> informal sector<br />

than for sWEEE collected through <strong>the</strong> ElektroG. For Germany, <strong>the</strong> following assumptions<br />

were used to quantify <strong>the</strong> <strong>flow</strong>s to reuse:<br />

50% <strong>of</strong> <strong>the</strong> sWEEE collected by <strong>the</strong> informal sector and by ‘o<strong>the</strong>rs’ is sent for reuse;<br />

50% <strong>of</strong> <strong>the</strong> end-<strong>of</strong>-life mobile phones collected by <strong>the</strong> producers is sent for reuse;<br />

5% <strong>of</strong> <strong>the</strong> end-<strong>of</strong>-life personal computers and 2% <strong>of</strong> <strong>the</strong> large high-grade equipment<br />

collected by <strong>the</strong> municipalities is sent for reuse;<br />

1% <strong>of</strong> <strong>the</strong> sWEEE belonging to <strong>the</strong> o<strong>the</strong>r three equipment groups collected by <strong>the</strong><br />

municipalities is sent for reuse.<br />

Table 24 summarizes <strong>the</strong> results. They include <strong>the</strong> parts <strong>of</strong> sWEEE sorted out for reuse<br />

before or during treatment (this <strong>flow</strong> <strong>of</strong> reused parts <strong>of</strong> sWEEE is assumed to be very <strong>small</strong>).<br />

The orders <strong>of</strong> magnitude <strong>of</strong> <strong>the</strong> data <strong>of</strong> Table 24 match <strong>the</strong> data reported by BMU (2008).

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