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Environmental and health related criteria for buildings - ANEC

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IBO - <strong>Environmental</strong> <strong>and</strong> Health <strong>related</strong> Criteria <strong>for</strong> Buildings<br />

Transports to <strong>and</strong> from sites (<strong>for</strong> construction, refurbishment, <strong>and</strong> removal of <strong>buildings</strong>) are<br />

required in an overall LCA. They contribute to only 4% of the total embodied non-renewable<br />

primary energy over the whole lifecycle. An overall assessment of primary energy does not<br />

allow differentiation. There<strong>for</strong>e, it is more effective to optimise the traffic-<strong>related</strong> energy<br />

consumption to <strong>and</strong> from site by indicators requiring the use of (low-emitting) vehicles with<br />

efficient diesel consumption than to limit the overall primary energy dem<strong>and</strong> over the<br />

lifecycle.<br />

8. LIFE CYCLE ASSESSMENT<br />

8.1. Introduction<br />

Scope<br />

<strong>ANEC</strong> has commissioned several studies <strong>and</strong> already <strong>for</strong>med its opinion about LCA as well<br />

as its application in building assessment. Hence, the following chapter concentrates on the<br />

compilation of the main findings in the relevant studies <strong>and</strong> on recommendations concerning<br />

the use of LCA in building assessment systems.<br />

A detailed analysis of the use of LCA in the existing building assessment systems is not<br />

carried out since LCA-methodology is clearly defined in ISO 14040 <strong>and</strong> 14044. The various<br />

building assessment systems differ concerning the used indicators, the considered life cycle<br />

stages <strong>and</strong> the weighting <strong>and</strong> benchmarking of the indicators. Besides, some findings about<br />

the use of LCA-indicators in building assessment systems were already listed in chapter<br />

“Energy <strong>and</strong> CO 2 -emission”.<br />

Hence, we preferred relying the conclusions <strong>and</strong> recommendations concerning the use of<br />

LCA in building assessment systems on the following meta-studies (see also chapter “3.2<br />

Background”):<br />

- European Commission / Joint Research Centre: <strong>Environmental</strong> improvement potential of<br />

residential <strong>buildings</strong> (IMPRO-Building, 2008)<br />

- European Commission / Joint Research Centre: <strong>Environmental</strong> Impact of Products<br />

(EIPRO). Analysis of the life cycle environmental impacts <strong>related</strong> to the final<br />

consumption of the EU-25 (EIPRO, 2006)<br />

- <strong>ANEC</strong> / Öko-Institut, Ökopol: <strong>Environmental</strong> product indicators <strong>and</strong> benchmarks in the<br />

context of environmental labels <strong>and</strong> declarations (PRAKASH, REINTJES, 2008)<br />

<strong>and</strong> on own experience with <strong>and</strong> knowledge of life cycle assessment of <strong>buildings</strong>.<br />

(Very) short introduction to life cycle assessment (LCA)<br />

Life cycle assessment (LCA) st<strong>and</strong>s <strong>for</strong> “compilation <strong>and</strong> evaluation of the inputs, outputs<br />

<strong>and</strong> the potential environmental impacts of a product system throughout its life cycle” (ISO<br />

14040). It is a technique to assess the environmental aspects <strong>and</strong> potential impacts<br />

associated with a product, process, or service, by:<br />

- compiling an inventory of relevant energy <strong>and</strong> material inputs <strong>and</strong> environmental releases<br />

(“LCI - Life Cycle Inventory”);<br />

Final Report 82 31 03 2011

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