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advanced building skins 14 | 15 June 2012 - lamp.tugraz.at - Graz ...

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2.1.4 SBTool<br />

Advanced Building Skins<br />

The SBTool 5 is based on the philosophy th<strong>at</strong> a r<strong>at</strong>ing system must be adapted to local conditions<br />

before its results can become meaningful. The system is therefore designed as a generic framework,<br />

with local non-commercial organiz<strong>at</strong>ions being expected to define local context conditions and to<br />

develop appropri<strong>at</strong>e weights and benchmarks. The system has been designed to facilit<strong>at</strong>e such a<br />

regional calibr<strong>at</strong>ion; in fact, the system requires the insertion of regionally meaningful benchmarks.<br />

SBTool covers a wide range of sustainable <strong>building</strong> issues, not just green <strong>building</strong> concerns, but the<br />

scope of the system can be modified to be as narrow or as broad as desired, ranging from 120 criteria<br />

to half a dozen;<br />

The system allows third parties to establish parameter weights th<strong>at</strong> reflect the varying importance of<br />

issues in the region, and to establish relevant benchmarks by occupancy type, in local languages. Thus,<br />

many versions can be developed in different regions th<strong>at</strong> look quite different, while sharing a common<br />

methodology and set of terms. The main advantage, however, is th<strong>at</strong> an SBTool version developed<br />

with local knowledge is likely to be much more relevant to local needs and values than other systems;<br />

The system provides separ<strong>at</strong>e modules for Site and Building assessments, with Site assessments<br />

carried out in the Pre-design phase and Building assessments carried out in Design, Construction or<br />

Oper<strong>at</strong>ions phases;<br />

SBTool takes into account region-specific and site-specific context factors, and these are used to<br />

switch off or reduce certain weights, as well as providing background inform<strong>at</strong>ion for all parties.<br />

Weights for criteria th<strong>at</strong> remain active are re-distributed, so th<strong>at</strong> the total always remains 100%.<br />

There is a capacity to carry out assessments <strong>at</strong> four distinct stages of the life-cycle and the system<br />

provides default benchmarks suited to each phase.<br />

2.2 N<strong>at</strong>ional Building Vertific<strong>at</strong>ion Systems in Austria<br />

2.2.1 Klima:aktiv (Building and Refurbishment)<br />

The klima:aktiv <strong>building</strong> and refurbishment certific<strong>at</strong>ion system for New Construction Office [30] is<br />

divided into four assessment c<strong>at</strong>egories according to a system of 1000 points. The c<strong>at</strong>egories are<br />

design and construction (C<strong>at</strong>egory A maximum 120 points), energy (C<strong>at</strong>egory B, maximum 600<br />

points), <strong>building</strong> m<strong>at</strong>erials and construction (C<strong>at</strong>egory C, maximum 160 points) and comfort and<br />

indoor air quality (C<strong>at</strong>egory D, maximum 120 points).<br />

Klima:aktiv assessment allows LCA to be carried out in two different ways. On the one hand, c<strong>at</strong>egory<br />

C 2.1a (ecological benchmark of the whole <strong>building</strong>) and altern<strong>at</strong>ive c<strong>at</strong>egory C 2.1b (ecological<br />

benchmark of <strong>building</strong> envelope). The assessment considers three environmental impact c<strong>at</strong>egories<br />

GWP, AP and PEI.n.e. (or CEDnr). For the final assessment these three environmental impact<br />

c<strong>at</strong>egories are aggreg<strong>at</strong>ed into one ecological benchmark (OI 3).<br />

In the first case, the assessment goes only partly in line with the CEN/TC 350 approach. The Use<br />

phase only focuses on environmental impacts. Due to the fact th<strong>at</strong> the construction and maintenance<br />

processes are considered by the assessment, environmental impacts caused by energy demand during<br />

use phase are not included in the aggreg<strong>at</strong>ed results. Environmental impacts are partly embedded in<br />

c<strong>at</strong>egory B 2.2 (CO2 emissions) and B 2.3 (cumul<strong>at</strong>ive energy demand).<br />

In the second case, due to time-rel<strong>at</strong>ed focus of the before use phase and the sp<strong>at</strong>ial-rel<strong>at</strong>ed focus of<br />

the <strong>building</strong> envelope as well as the declar<strong>at</strong>ion of environmental impacts in CO2-emissions, the<br />

environmental assessment concept does not correspond to the CEN/TC 350 concept, which is based on<br />

a holistic approach. The influence of neglecting sp<strong>at</strong>ial and/or time rel<strong>at</strong>ed aspects is shown in detail in<br />

[5].<br />

At most, 100 points (or 10%) can be achieved by using case one, and 75 points can be reached by<br />

accomplishing LCA in case two. Taking into account the previously mentioned c<strong>at</strong>egories B 2.2 (125<br />

points) and B 2.3 (125 points), a total of 350 points using case one, and 325 points using case two, can<br />

be achieved.<br />

5 Overview of the SBTool assessment framework, Nils Larsson, iiSBE and Manuel Macias, UPM Spain, April <strong>2012</strong><br />

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