04.10.2012 Aufrufe

2 > Methodische Grundlagen

2 > Methodische Grundlagen

2 > Methodische Grundlagen

MEHR ANZEIGEN
WENIGER ANZEIGEN

Sie wollen auch ein ePaper? Erhöhen Sie die Reichweite Ihrer Titel.

YUMPU macht aus Druck-PDFs automatisch weboptimierte ePaper, die Google liebt.

Summary 17<br />

> Summary<br />

According to ISO Standard 14040, the life cycle assessment (LCA) of products,<br />

processes or companies comprises four phases:<br />

> Goal and scope definition<br />

> Inventory analysis<br />

> Impact assessment and<br />

> Interpretation.<br />

The “ecological scarcity” method permits impact assessment of life cycle inventories<br />

according to the “distance to target” principle. Eco-factors, expressed as eco-points per<br />

unit of pollutant emission or resource extraction, are the key parameter used by the<br />

method. With that method, eco-factors are determined by the current emissions<br />

situation and, secondly, by the political targets set by Switzerland or by international<br />

policy and supported by Switzerland.<br />

The eco-factors proposed for various environmental impacts in the first update of the<br />

method (Brand et al. 1998) are used widely. The fresh update presented here became<br />

necessary to reflect new scientific findings, new statutory and political targets, new<br />

international agreements, developments in international standarization and experience<br />

gathered in practice. As a part of this revision, the eco-factor formula has been adjusted<br />

to the structure of the ISO standard (with its elements of charactization, normalization<br />

and weighting). The set of substances assessed has been further enlarged. The data and<br />

information on which the existing eco-factors were based was checked and updated.<br />

The key changes made are as follows:<br />

> The mathematical representation of the ecofactor formula has been slightly modified.<br />

The characterization step is now made explicit. In addition, normalization is<br />

now based on current emissions, as has become common practice. As a consequence<br />

the weighting factor ( ratio of current to critical flow) is squared. With both the old<br />

and new formula representation, the resulting eco-factors remain identical if the data<br />

is the same.<br />

> With regard to CO2 and energy, the long-term target of the Swiss confederation (1<br />

tonne CO2 or 2000 W per capita) was interpolated for the year 2030, which is a<br />

common time horizon of Swiss legislation.<br />

> With regard to air pollutants, new eco-factors were determined for benzene, dioxin<br />

and diesel soot, based on the precautionary principle enshrined in the Swiss<br />

Environmental Protection Act.<br />

> For heavy metal emissions (both to air and to soil), the long-term maintenance of<br />

soil fertility is now used as the new target.<br />

> Eco-factors can now be defined according to regional scarcities, if needed and if<br />

regional data are available. This principle is applied to phosphorus and emissions<br />

to Swiss surface waters.

Hurra! Ihre Datei wurde hochgeladen und ist bereit für die Veröffentlichung.

Erfolgreich gespeichert!

Leider ist etwas schief gelaufen!