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 />
Hybrid LCA can be used to estimate the embodied impacts of traded goods and services. While<br />
national SRIO hybrid LCA studies have been described in the literature, no trade specific analysis has<br />
yet been published. However, it is conceivable that process-based analyses of international supply<br />
chains could be combined with data from MRIO models. Such a method would especially be suited to<br />
complex commodities.<br />
From a statistical point of view, process LCA data play three roles: firstly, to provide "disaggregation<br />
factors" that allow representation of NAMEA data at a lower aggregation level than allowed by the<br />
confidentiality restrictions on the original NAMEA data, and at lower levels than possible from the way<br />
NAMEA data are collected. Secondly, process-specific emission factors can help to replace or qualify<br />
average emission intensities of IO sectors. And thirdly, Life Cycle Impact Assessment (LCIA) provides<br />
characterisation factors needed to express environmental pressures as impacts (see Section 4.5.1).<br />
Below we provide several examples of recent hybrid LCA studies 17 to demonstrate the feasibility<br />
and usefulness of such approaches, even if they do not explicitly deal with traded goods and services.<br />
Benders et al. (2001) developed a tiered hybrid analysis tool for determining energy use and<br />
greenhouse gas emissions related to household consumption items focussing on reduction in energy<br />
use and greenhouse gas emissions. This tool, the energy analysis program (EAP), is a computer<br />
program that consists of a number of fill-in screens corresponding to steps in a hybrid method<br />
(developed by van Engelenburg et al. 1994) in which some main steps are covered with LCA data and<br />
some minor steps with input-output data. One of the applications of the program concerns the<br />
calculation of the total energy requirement of Dutch households by combining household budget data<br />
with energy intensities of about 350 products and services (Biesiot and Moll 1995).<br />
The environmental assessment study of Swedish agriculture presented by Engström et al. (2007) is a<br />
classical example of tiered hybrid analysis where SRIO model data are extended or replaced with<br />
process LCA data. This is done for the purpose of specifying emission intensities (such as for N 2 O<br />
emissions from the production of nitrogen fertilizers which fall under the broad IO sector of 'chemical<br />
products) or for extending pressure variables to LCA impact categories such as global warming,<br />
acidification, eutrophication and so on.<br />
Similar tiered hybrid analyses have been run by Kofoworola and Gheewala (2008) for the life cycle<br />
assessment of an office building in Thailand or by Junnila (2008) for the life cycle management of<br />
energy-consuming products. In these cases LCA data describe site-specific processes that replace IO<br />
data or augment these by adding downstream life cycle impacts to the system.<br />
The quantification of impacts from international transportation is an important area for tiered hybrid<br />
analysis using process data. The main question is how to assign emissions from the combustion of<br />
fuels from bunkers for international aviation and shipping. From a production perspective (such as<br />
when following SNA93 principles; United Nations Statistics Division 1993), bunker emissions should<br />
be assigned to ship or plane operators’ country of domicile and – in the case of passenger transport –<br />
counted as exports if passengers are non-resident, otherwise as domestic consumption. From a<br />
consumption perspective (as taken by an <strong>EIPOT</strong> MRIO model), emissions of residents using<br />
international passenger transport should be counted as consumption emissions of their country. For<br />
goods, bunker emissions from imports are allocated to country of import and bunker emissions from<br />
exports are not counted. In any case a bottom-up approach using process data is needed, which<br />
requires the following information:<br />
17<br />
The selection is non-exhaustive.<br />
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