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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impact category shall be a maximum start<strong>in</strong>g po<strong>in</strong>t. It is, however, stressed that<br />
the cut-off rule does not apply to hazardous <strong>and</strong> toxic substances.<br />
Allocation issues<br />
As a specific detail, the PCR-document specifies that for materials that do not<br />
change their <strong>in</strong>herent properties dur<strong>in</strong>g recycl<strong>in</strong>g, the end-of-life actual recycl<strong>in</strong>g<br />
rate usually is the <strong>environmental</strong>ly more appropriate parameter to quantify the<br />
recycl<strong>in</strong>g aspect <strong>in</strong>stead of recycled content.<br />
2.4.2 LCA/LCI-<strong><strong>in</strong>formation</strong> to be <strong>in</strong>cluded<br />
The follow<strong>in</strong>g <strong>environmental</strong> <strong><strong>in</strong>formation</strong> is suggested to be <strong>in</strong>cluded <strong>in</strong> the EPD.<br />
• Environmental impacts expressed <strong>in</strong> terms of the impact categories of<br />
LCIA<br />
o climate change<br />
o destruction of the stratospheric ozone layer;<br />
o acidification of l<strong>and</strong> <strong>and</strong> water sources;<br />
o eutrophication;<br />
o formation of tropospheric ozone (photochemical oxidants).<br />
o depletion of non-renewable energy resources;<br />
o depletion of non-renewable material resources;<br />
• Use of resources <strong>and</strong> renewable primary energy — Data derived from<br />
LCI <strong>and</strong> not assigned to the impact categories of LICIA<br />
o use of renewable material resources;<br />
o use of renewable primary energy;<br />
o consumption of freshwater.<br />
• Waste to disposal — Data derived from LCA <strong>and</strong> not assigned to the<br />
impact categories of LCIA. The waste allocated to the build<strong>in</strong>g product<br />
dur<strong>in</strong>g its life cycle shall be classified <strong>in</strong> the EPD as<br />
o hazardous waste, or<br />
o non-hazardous waste<br />
• Emissions to water <strong>and</strong> <strong>in</strong>door air<br />
o To be declared <strong>in</strong> accordance with national st<strong>and</strong>ards <strong>and</strong><br />
practice. Information on human health <strong>and</strong> comfort due to<br />
chemical, biological <strong>and</strong> physical emissions is required for further<br />
evaluation on the build<strong>in</strong>g level of human health <strong>and</strong> comfort.<br />
When compared to ISO 14025 <strong>and</strong> ISO/FDIS 21930 it can be noticed that there<br />
are some differences <strong>in</strong> the assignments <strong>and</strong> term<strong>in</strong>ology used. In CEN TC 350<br />
depletion of non-renewable energy <strong>and</strong> material resources is thus considered to<br />
be an impact category, while <strong>in</strong> the ISO-st<strong>and</strong>ards it is considered as <strong>in</strong>ventory<br />
<strong><strong>in</strong>formation</strong>. Another difference is that CEN TC 350 addresses the “destruction”<br />
of the stratospheric ozone layer, whereas the ISO-st<strong>and</strong>ards address its<br />
“depletion”.<br />
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