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 />
Equation 1<br />
e<br />
j<br />
= e<br />
j1<br />
with g<br />
j<br />
+ e<br />
j 2<br />
= g<br />
j1<br />
g<br />
=<br />
g<br />
+ g<br />
j1<br />
j<br />
j 2<br />
e<br />
j<br />
+<br />
g<br />
g<br />
j 2<br />
j<br />
e<br />
j<br />
As a direct consequence, CO 2 intensities d j1 and d j2 in these sub-sectors will be equal to the CO 2<br />
intensity in the aggregate sector d j , that is<br />
e<br />
j1<br />
e<br />
j<br />
e<br />
j 2<br />
Equation 2 d<br />
j1 = = = d<br />
j<br />
= = d<br />
j2<br />
g g g<br />
j1<br />
j<br />
j2<br />
The next best possibility is to use the information from more disaggregated environmental accounts<br />
from other countries or data sources (see Druckman and Jackson 2008).<br />
If the detail of the input-output data is not sufficient, data from other countries or regions can also be<br />
used. An example is the EIPRO project (Tukker et al. 2006) in which the environmental impacts of<br />
consumption in EU-25 were determined by Europeanising the US CEDA model. Since for Europe no<br />
detailed input-output table was available (the 35 sector OECD IO table was used), the structure of the<br />
480 sector was used to receive more detail in the calculations.<br />
As explained above, the EU-FP6-project EXIOPOL is setting up an environmentally extended IO<br />
framework disaggregated into about 130 sectors. As generally such detailed IO tables are not<br />
available, various transformations and estimations are necessary to complete national datasets, reach<br />
this level of disaggregation and harmonise existing SUTs. The following list summarises the<br />
approaches used (Tukker and Heijungs 2007a):<br />
Completing the basic dataset<br />
• Using SIOT to construct a fully absent SUT.<br />
• Estimating valuation matrices that can convert a use table in purchaser’s prices into basic prices.<br />
• Estimating import matrices (assuming proportional use of domestic and imported products in all<br />
sectors; or using known import matrices from ‘similar’ countries).<br />
• Estimating missing and confidential data. For example, some NSIs ‘hide’ certain cells in their SUTs<br />
and SIOTs.<br />
• Estimating data of missing countries via ‘similar’ countries.<br />
Harmonizing SUT across countries<br />
• Mapping the country SUT on the EXIOPOL classification (many-to-one => aggregation; one-tomany<br />
=> sectors/products split up; many-to-many => split up and re-allocation to EXIOPOL<br />
classification).<br />
• Adjusting to a common base year. Scaling up or down the SUT to match the base year output.<br />
• Adjusting to a common unit (monetary).<br />
• Estimating data of missing countries via ‘similar’ countries.<br />
Detailing sectors<br />
• Using data on environmental extensions, energy statistics technology transfer assumptions from<br />
countries with detailed tables.<br />
5.2.3 Updating data and the production of time series<br />
As mentioned above, the publication of IO tables and environmental data always lags a few years<br />
behind the current year and symmetric IO tables are normally only constructed every five years. For<br />
the purpose of (environmental) analyses, it is advantageous to have up-to-date information to inform<br />
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