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Technical Development of Waste Sector in Sweden: Survey

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

Figure 3: Conceptual frame work <strong>of</strong> def<strong>in</strong><strong>in</strong>g categories <strong>in</strong>dicator (CML, 2001)<br />

Life cycle <strong>in</strong>ventory results are analyzed based on impact categories. Characterization model and<br />

environmental impacts are considered for the model as the midpo<strong>in</strong>t analysis <strong>in</strong> the CML method. In<br />

SimaPro s<strong>of</strong>tware, CML model analyzes potential environmental impact us<strong>in</strong>g the follow<strong>in</strong>g different<br />

impact categories:<br />

• Abiotic Depletion<br />

• Acidification<br />

• Eutrophication<br />

• Global Warm<strong>in</strong>g<br />

• Ozone Layer Depletion<br />

• Human Toxicity<br />

• Fresh Water Ecotoxicity<br />

• Mar<strong>in</strong>e Ecotoxicity<br />

• Terrestrial Ecotoxicity<br />

• Photochemical Oxidation<br />

Characterization <strong>in</strong> LCA model gives the idea on how much environmental burden, the process or<br />

product contributes to the environment. Normalization value implies the level <strong>of</strong> significance based<br />

on reference normalization values. In CML method, different normalization values like West Europe<br />

(1995), Netherlands (1997) or World (1995) can be considered. In this study, West Europe (1995)<br />

values are considered for the model. Table 2 shows the different reference normalization value.<br />

KUNGLIGA TEKNISKA HÖGSKOLAN<br />

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