EIPOT Final Project Report - Stockholm Environment Institute
EIPOT Final Project Report - Stockholm Environment Institute
EIPOT Final Project Report - Stockholm Environment Institute
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ERA-NET SKEP <strong>Project</strong> <strong>EIPOT</strong> (www.eipot.eu)<br />
“Development of a methodology for the assessment of global environmental impacts of traded goods and services”<br />
2.3 Spatial dimension<br />
The third dimension is geography, which considers the spatial aspect of trade and the distribution of its<br />
impacts. Naturally, any method that aims to quantify and assess the impacts of international trade<br />
needs to be able to distinguish countries or regions of origin and destination as well as their economic<br />
structure and production technologies and efficiencies. The geographical scope and the number of<br />
countries and sectors considered is therefore an important factor in the evaluation of <strong>EIPOT</strong> methods.<br />
Furthermore, the method should be able to assess environmental pressures that cannot be allocated<br />
directly to countries, such as emissions of international transport by water and air.<br />
Although the original focus of the <strong>EIPOT</strong> project was to build a method for SKEP countries, we aim at<br />
formulating a more general framework that is in principle applicable to any country or region. One<br />
example is the Mediterranean region where a list of actions has been proposed for applying the<br />
consumption-based approach to GHG emissions (CP/RAC 2008). Ultimately, the feasibility of<br />
implementing a method in or for a particular country will depend on data availability. This issue is<br />
discussed in Chapter 5.<br />
2.4 Temporal dimension<br />
Time is the fourth dimension that needs to be considered. Temporal issues determine policy questions<br />
and in turn the choice of methodology or model that is able to address these questions. 9 The methods<br />
shown in Figure 2.1 are all ex-post approaches that use data from the past to enumerate previous<br />
environmental impacts. Often the results are used as an approximation for present time impacts of<br />
production or consumption. This is sufficient to establish the current hotspots of pressures or impacts<br />
and to devise environmental or SCP policies that address current production and consumption<br />
patterns. However, if the goal is to anticipate future impacts or test the effect of specific policies (such<br />
as taxation, trade tariffs, carbon trading, government spending), scenario or dynamic modelling or a<br />
combination of both needs to be employed. To cover this policy field, econometric and dynamic<br />
models with explicit coverage of international trade were included in the RACER analysis of the <strong>EIPOT</strong><br />
project (Lutter et al. 2008).<br />
2.5 Life cycles<br />
The fifth dimension concerns another system boundary aspect, namely the life cycle stages of traded<br />
goods. When performing a life cycle assessment of a product, upstream production impacts during the<br />
cradle-to-gate or cradle-to-shelf phase need to be included as well as downstream impacts during the<br />
use and disposal phase (cradle-to-grave). When comparing products, impacts in all life cycle stages<br />
should be considered. The lifetime of a product becomes important in its use phase and methods<br />
need to attribute impacts accordingly. With regard to trade, the use phase and/or disposal phase may<br />
be (partly) abroad, such as tourist trips or the export of waste to developing countries.<br />
At the macro and meso levels, there should be consistency between the stages. Where materials are<br />
recycled in the disposal stage and re-enter the production chain, this should be accounted for in the<br />
use of primary and secondary materials in the material stage.<br />
9<br />
Compare to the categorisation of tools for sustainability assessment by Ness et al. (2007).<br />
13