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LCA of an Ecolabeled Notebook - GreenDeltaTC

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Goal <strong>an</strong>d Scope<br />

Stakeholder group society:<br />

Table 10: Indicators <strong>of</strong> the stakeholder society for background processes<br />

Source: own, referring to UNEP/SETAC Life Cycle Initiative (2010)<br />

40<br />

Subcategory Indicators<br />

Public commitments<br />

to sustainable issues<br />

Contribution to economic<br />

development<br />

Prevention <strong>an</strong>d<br />

mitigation <strong>of</strong> conflicts<br />

Technology<br />

development<br />

� Presence <strong>of</strong> publicly available promises or agreements on sustainable<br />

issues <strong>an</strong>d complaints to the non fulfilment <strong>of</strong> these commitments<br />

� Implementation/signing <strong>of</strong> principles or codes <strong>of</strong> conducts<br />

� Economic situation <strong>of</strong> the country <strong>an</strong>d relev<strong>an</strong>ce <strong>of</strong> the considered<br />

sector for the economy<br />

� Presence <strong>of</strong> conflicts in the country<br />

� Risk <strong>of</strong> conflicts with regard to the sector 38 <strong>an</strong>d measures <strong>of</strong> the<br />

sector to reduce the risk<br />

� Sector efforts in technology development regarding ec<strong>of</strong>riendliness<br />

� Investments in technology development<br />

Corruption � Risk <strong>of</strong> corruption in country/sector<br />

2.2.4.1.3 Social Impact Assessment<br />

The study performs <strong>an</strong> environmental <strong>an</strong>d a social impact assessment. For E-LCIA, predefined<br />

impact assessment methods exist, as for inst<strong>an</strong>ce CML, Eco-indicator, Traci, or<br />

ReCiPe. These methods have been broadly discussed in the scientific community.<br />

For S-LCIA, the situation is very different as there are no internationally accepted impact<br />

assessment methods available. <strong>GreenDeltaTC</strong> developed a first impact assessment<br />

method for social impacts, which is able to consider both qu<strong>an</strong>titative <strong>an</strong>d qualitative<br />

data. 39 This impact assessment method is also applied in this project. The procedure <strong>of</strong><br />

the method is explained in detail in the following, to ensure replicability <strong>an</strong>d tr<strong>an</strong>sparency.<br />

There are two types <strong>of</strong> impact categories in <strong>LCA</strong>: endpoints <strong>an</strong>d midpoints. While midpoint<br />

categories model immediate effects as ozone depletion, acidification, or hum<strong>an</strong><br />

toxicity, endpoint categories aim to consider the ”final impact” on the areas <strong>of</strong> protection<br />

hum<strong>an</strong> health, environment, <strong>an</strong>d resources. The developed S-LCIA method considers<br />

exclusively midpoints, because the use <strong>of</strong> endpoints implies the aggregation <strong>of</strong> results,<br />

which in turn reduces tr<strong>an</strong>sparency <strong>an</strong>d increases uncertainty. Furthermore, in<br />

38<br />

For inst<strong>an</strong>ce, (potential) conflicts due to the depletion <strong>of</strong> rare resources, massive pollution, or<br />

poor labour st<strong>an</strong>dards.<br />

39<br />

Fr<strong>an</strong>ze/Ciroth (2009)

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