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102 Substance <strong>flow</strong> <strong>analysis</strong> <strong>of</strong> <strong>the</strong> <strong>recycling</strong> <strong>of</strong> <strong>small</strong> WEEE<br />

6.1.2. Collection<br />

In Germany, legislative requirements provide <strong>the</strong> main motivation for collection, reuse and<br />

treatment <strong>of</strong> WEEE. The current collection target <strong>of</strong> 4 kg per year and capita does not set<br />

incentives to increase <strong>the</strong> collection <strong>of</strong> WEEE, because this collection target was already<br />

achieved in Germany in 2000 (long before <strong>the</strong> implementation <strong>of</strong> <strong>the</strong> ElektroG), where<br />

476 000 tonnes <strong>of</strong> electronic <strong>waste</strong> appliances were collected (BMU 2007). Moreover, <strong>the</strong><br />

collection target is not differentiated according to <strong>the</strong> equipment types, so that it does not<br />

promote <strong>the</strong> collection <strong>of</strong> <strong>small</strong> and light devices, but <strong>the</strong> collection <strong>of</strong> heavy appliances<br />

(Rotter et al. 2006). However, <strong>the</strong> regulations define how collection should be performed and<br />

who is responsible for financing <strong>the</strong> operations, so that collection systems are in place for all<br />

types <strong>of</strong> <strong>waste</strong> equipment including <strong>the</strong> <strong>small</strong> ones. In <strong>the</strong> USA, where little legislation<br />

regulates <strong>the</strong> <strong>recycling</strong> <strong>of</strong> WEEE, collection and treatment are mainly driven by <strong>the</strong> economy<br />

and by voluntary environmental protection for equipment types with a high hazardous<br />

potential, like CRT monitors. If maximising <strong>the</strong> revenues from <strong>the</strong> production <strong>of</strong> secondary<br />

raw materials is <strong>the</strong> primary focus, mainly very high-grade equipment like mobile phones and<br />

personal computers are collected for treatment or reuse. Because <strong>the</strong>re is little motivation to<br />

collect low-grade equipment, <strong>the</strong> collection rate for this equipment group is almost zero. In<br />

this sense, <strong>the</strong> different legislative frameworks explain <strong>the</strong> higher collection rates in Germany<br />

than in <strong>the</strong> USA.<br />

Regarding non-separated collection <strong>of</strong> sWEEE, a clear correlation between average size <strong>of</strong><br />

<strong>the</strong> WEEE and percentage <strong>of</strong> end-<strong>of</strong>-life devices disposed <strong>of</strong> by <strong>the</strong> last user was identified,<br />

as illustrated for Germany in Figure 32. To estimate <strong>the</strong> average size <strong>of</strong> <strong>the</strong> devices,<br />

quantified as <strong>the</strong> diagonal length, <strong>the</strong> data <strong>of</strong> <strong>the</strong> database described in chapter 3.3.1 were<br />

used. The <strong>small</strong>er <strong>the</strong> device, <strong>the</strong> more likely it is to be disposed <strong>of</strong> by <strong>the</strong> last user. The<br />

economic value <strong>of</strong> <strong>the</strong> device also plays a role in <strong>the</strong> discard behaviour <strong>of</strong> <strong>the</strong> user, as well<br />

as o<strong>the</strong>r factors like <strong>the</strong> emotional value, or <strong>the</strong> identification <strong>of</strong> <strong>the</strong> user with <strong>the</strong> device that<br />

is not only used for its function but primarily as a “life-style companion”. Low-grade<br />

equipment is more likely to be disposed <strong>of</strong> than large high-grade equipment (Figure 32).

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