Benchmarking and additional environmental information in ... - ANEC
Benchmarking and additional environmental information in ... - ANEC
Benchmarking and additional environmental information in ... - ANEC
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For comfort aspects relevant characteristics (mechanical, physical, chemical,<br />
thermal, acoustic properties …) shall be selected <strong>and</strong> declared for each type of<br />
comfort (hydrothermal, acoustic, visual, <strong>and</strong> olfactory). Suitable test methods<br />
are suggested <strong>in</strong> an Annex to the st<strong>and</strong>ard.<br />
2.7.4 Presentation of results<br />
EPD’s established accord<strong>in</strong>g to NF P-0-010 are presented <strong>in</strong> an (almost) fixed<br />
format with the head<strong>in</strong>gs <strong>in</strong>dicated above com<strong>in</strong>g <strong>in</strong> the same sequence. With<br />
the requirement of report<strong>in</strong>g the <strong>in</strong>ventory results <strong>in</strong> detail, the EPD’s become<br />
very extensive be<strong>in</strong>g <strong>in</strong> the range of about 40 pages.<br />
2.8 The Swedish EPD® scheme<br />
The general requirements for <strong>environmental</strong> product declarations <strong>in</strong> the<br />
Swedish EPD system have been def<strong>in</strong>ed by the Swedish Environmental<br />
Management Council (Miljöstyrn<strong>in</strong>gsrådet, 2000) (MSR 1999:2). The system<br />
has a broad scope, <strong>in</strong>clud<strong>in</strong>g common consumer products like roof boxes for<br />
cars, cooker hoods <strong>and</strong> sanitation goods as well as B2B products like basic<br />
metals <strong>and</strong> transformers. In total, 25 product categories have been def<strong>in</strong>ed so<br />
far <strong>and</strong> different sets of product category rules have been developed with<strong>in</strong><br />
these product groups.<br />
2.8.1 LCA approach<br />
The general LCA approach conforms to the requirements <strong>in</strong> the ISO 14040<br />
series <strong>and</strong> ISO 14025.<br />
Life cycle stages<br />
Accord<strong>in</strong>g to MSR 1999:2, the EPD shall consider all stages from cradle-tograve.<br />
However due to lack of detailed <strong><strong>in</strong>formation</strong> on how a product is<br />
distributed, used <strong>and</strong> h<strong>and</strong>led at the end of its life cycle, the quantitative<br />
<strong><strong>in</strong>formation</strong> shall be separated for the phases that describe the results of the<br />
LCA study from raw material acquisition to manufactured product on one h<strong>and</strong>,<br />
<strong>and</strong> distribution to the market, product use, recovery, recycl<strong>in</strong>g <strong>and</strong> waste<br />
h<strong>and</strong>l<strong>in</strong>g on the other. Based on a quick exam<strong>in</strong>ation of available EPD’s, this<br />
approach is not followed <strong>in</strong> all cases. In fact, it seems like the way of present<strong>in</strong>g<br />
results is chosen somewhat arbitrarily – perhaps as a consequence of<br />
deviations from the general approach <strong>in</strong> the specific product category rules.<br />
Consequential or attributional LCA<br />
The data shall be expressed as annual average values. Plant-specific data from<br />
manufactur<strong>in</strong>g processes should always be used, <strong>and</strong> generic data should be<br />
used <strong>in</strong> cases where they are representative for the purpose of the study, e.g.<br />
purchase of bulk <strong>and</strong> raw materials on the spot market <strong>and</strong> <strong>in</strong> the use- or waste<br />
h<strong>and</strong>l<strong>in</strong>g stages. This approach is considered to be attributional.<br />
Cut-off rules<br />
The loss of <strong><strong>in</strong>formation</strong>, as a result of omitt<strong>in</strong>g processes from the LCA study<br />
can be accepted provided that the sum of the loss of <strong><strong>in</strong>formation</strong> corresponds to<br />
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