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Technical Development of Waste Sector in Sweden: Survey

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MASTER’S THESIS IN ENVIRONMENTAL STRATEGIES RESEARCH<br />

Table 2: Normalization value <strong>in</strong> different impact categories <strong>in</strong> CML method<br />

Adopted LCA themes Unit West<br />

Europe,<br />

1995<br />

The<br />

Netherlands,<br />

1997<br />

World,<br />

1995<br />

Abiotic depletion kg Sb eq 6.76E-11 5.85E-10 6.39E-12<br />

Acidification kg SO2 eq 3.66E-11 1.49E-9 3.11E-12<br />

Eutrophication kg PO4--- eq 8.02E-11 1.99E-9 7.56E-12<br />

Global warm<strong>in</strong>g (GWP100) kg CO2 eq 2.08 E-13 3.96E-12 2.41E-14<br />

Ozone layer depletion (ODP) kg CFC-11 eq 1.20E-8 1.02E-6 1.94E-9<br />

Human toxicity kg 1,4-DB eq 1.32E-13 5.32E-12 1.75E-14<br />

Fresh water aquatic ecotox. kg 1,4-DB eq 1.98E-12 1.33E-10 4.90E-13<br />

Mar<strong>in</strong>e aquatic ecotoxicity kg 1,4-DB eq 8.81E-15 3.14E-13 1.95E-15<br />

Terrestrial ecotoxicity kg 1,4-DB eq 2.12E-11 1.09E-9 3.72E-12<br />

Photochemical oxidation kg C2H4 1.21E-10 5.49E-9 1.04E-11<br />

SimaPro, 2007<br />

For this study, west Europe 1995 normalized data was considered as the basel<strong>in</strong>e normalization data<br />

for the LCA model. Therefore, the normalization values showed <strong>in</strong> the LCA results, mean<strong>in</strong>g that,<br />

significant <strong>of</strong> the different impact categories were compared with West Europe per person emission<br />

unit.<br />

KUNGLIGA TEKNISKA HÖGSKOLAN<br />

11 | Page

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