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7. Recommendations 123<br />

Reuter et al. (2005) criticised some research methods <strong>of</strong> <strong>the</strong> field <strong>of</strong> industrial ecology, to<br />

which MFA and SFA belong, by saying that “industrial ecology so far has not or only partly<br />

bridged <strong>the</strong> gap between its holistic concepts and <strong>the</strong> different industrial practices”. Bridging<br />

this gap is a challenge and requires a close collaboration between <strong>the</strong> research and <strong>the</strong><br />

industry. From <strong>the</strong> industry, data and information on <strong>the</strong> practices are required. The research<br />

community should communicate more on <strong>the</strong> importance <strong>of</strong> research on industrial ecology<br />

and on its ability to deliver very useful findings for policy-support. Discussing <strong>the</strong> reliability <strong>of</strong><br />

<strong>the</strong> data and presenting <strong>the</strong> uncertainties are essential to increase <strong>the</strong> credibility <strong>of</strong> <strong>the</strong><br />

studies. Unfortunately, many MFA are published without a discussion <strong>of</strong> <strong>the</strong> reliability <strong>of</strong> <strong>the</strong><br />

data and <strong>the</strong> uncertainties <strong>of</strong> <strong>the</strong> results.<br />

Fur<strong>the</strong>r investigations are needed to complete <strong>the</strong> results and to quantify <strong>the</strong> <strong>flow</strong>s <strong>of</strong> o<strong>the</strong>r<br />

substances and in o<strong>the</strong>r geographical areas. The recovery and discarding rates for palladium<br />

presented in Table 34 are probably similar to <strong>the</strong> recovery and discarding rates for o<strong>the</strong>r<br />

trace metals like tin, antimony or nickel, because <strong>the</strong>se metals are recovered in <strong>the</strong> same<br />

recovery facilities. The results presented in this <strong>the</strong>sis <strong>of</strong> <strong>the</strong> <strong>flow</strong>s <strong>of</strong> palladium and gold can<br />

not be transferred to quantify <strong>the</strong> <strong>flow</strong>s <strong>of</strong> o<strong>the</strong>r materials like basis metals and plastics. The<br />

applied method is not only useful for assessing <strong>the</strong> recovery <strong>of</strong> valuable substances, but also<br />

for quantifying <strong>the</strong> amount <strong>of</strong> hazardous substances (for example mercury or brominated<br />

flame retardants) that is disposed <strong>of</strong> in an environmentally-sound way versus direct releases<br />

to <strong>the</strong> environment. In addition to <strong>the</strong> quantification <strong>of</strong> <strong>the</strong> material <strong>flow</strong>s, future research can<br />

be combined with o<strong>the</strong>r methods like life-cycle assessment (Tukker et al. 1997) or social<br />

sciences modelling (Binder 2007), to provide more pr<strong>of</strong>ound information for policy-making.

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