advanced building skins 14 | 15 June 2012 - lamp.tugraz.at - Graz ...
advanced building skins 14 | 15 June 2012 - lamp.tugraz.at - Graz ...
advanced building skins 14 | 15 June 2012 - lamp.tugraz.at - Graz ...
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Primary energy,<br />
non renewable<br />
kWh per m² GFA<br />
75<br />
50<br />
25<br />
0<br />
‐25<br />
‐50<br />
‐75<br />
‐100<br />
‐125<br />
‐<strong>15</strong>0<br />
‐175<br />
‐200<br />
‐225<br />
‐250<br />
Advanced Building Skins<br />
0 2 4 6 8 10 12 <strong>14</strong> 16 18 20 22 24 26 28<br />
‐100<br />
30 years<br />
- 7 -<br />
Greenhouse gas<br />
emissions<br />
kg CO 2‐Equ. per m² GFA<br />
EPS (30 kg/m³) PE‐non‐ren. Wood fibre PE‐non‐ren.<br />
Glass wool PE‐non‐ren. Flax board PE‐non‐ren.<br />
EPS (30 kg/m³) GWP100 Wood fibre GWP100<br />
Glass wool GWP100 Flax board GWP100<br />
Figure 3: Ecological profile of insul<strong>at</strong>ion m<strong>at</strong>erials per square meter gross floor area. Comparison of opaque PH<br />
skin Mühlweg-C with LEH-skin scenario 5-a. Differences of nonrenewable primary energy demand and<br />
greenhouse gas emissions per gross floor area (GFA) for production, disposal and 30 years <strong>building</strong> oper<strong>at</strong>ion.<br />
2.3 Differences of LC-D<strong>at</strong>abases<br />
A sensitivity analysis was done for the assessment of insul<strong>at</strong>ion m<strong>at</strong>erials by comparing different<br />
d<strong>at</strong>abases with life cycle impact d<strong>at</strong>a for insul<strong>at</strong>ion m<strong>at</strong>erials. The d<strong>at</strong>a for production (cradle to g<strong>at</strong>e<br />
analysis) and production combined with end of life processes were analyzed. D<strong>at</strong>abases Ökobau.d<strong>at</strong><br />
2009 (ÖBD) [5], Ecoinvent 2.2 (ECOINV) [7] and Baubook [8] have been compared. Major<br />
differences of the methodology behind the d<strong>at</strong>abases are:<br />
Energy mix (electrical energy mix) for production and for environmental credits of thermal<br />
tre<strong>at</strong>ment with combined he<strong>at</strong> and power gener<strong>at</strong>ion.<br />
Share of secondary raw m<strong>at</strong>erials: E.g. the share of waste glass for glass wool production is<br />
65 % in Ecoinvent and 0 % in Ökobau.d<strong>at</strong>.<br />
CO2 intake of biogenic m<strong>at</strong>erial by photosynthesis: Considered in Ökobau.d<strong>at</strong> and Baubook<br />
Environmental credits <strong>at</strong> end of life:<br />
o Ökobau.d<strong>at</strong> includes environmental credits e.g. the end-of-life process for wood fiber<br />
boards is thermal waste tre<strong>at</strong>ment with combined he<strong>at</strong> and power gener<strong>at</strong>ion th<strong>at</strong> substitute<br />
electrical energy (German mix) and fossil gas.<br />
o Ecoinvent does not consider environmental credits. The recovery of energy by thermal<br />
waste tre<strong>at</strong>ment is considered within the process(es) for waste tre<strong>at</strong>ment and improves the<br />
energy mix.<br />
o Baubook does not include end of life processes<br />
Generally there are considerable differences for all insul<strong>at</strong>ion m<strong>at</strong>erials and the range and r<strong>at</strong>io of<br />
impact d<strong>at</strong>a are varying for each m<strong>at</strong>erial (figure 4):<br />
30<br />
20<br />
10<br />
0<br />
‐10<br />
‐20<br />
‐30<br />
‐40<br />
‐50<br />
‐60<br />
‐70<br />
‐80<br />
‐90