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LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

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GROUP 6, SESSION B: METHODS, TOOLS, DATABASES 8 th Int. Conference on <strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

908<br />

165. Subcategory assessment m<strong>et</strong>hod: stakeholder workers<br />

Paola Kar<strong>in</strong>a Sánchez Ramirez 1,* , Luigia P<strong>et</strong>ti 1 , Cássia Maria Lie Ugaya 2<br />

1 Department of Economic Studies, Università degli Studi "G. D'Annunzio", Pescara, Italy, 2 Technological<br />

Federal University of Parana, Curitiba, Brazil, * Correspond<strong>in</strong>g author. E-mail: p.sanchez@unich.it<br />

Social Life Cycle Assessment (S-<strong>LCA</strong>) is a technique to evaluate potential positive and negative impacts<br />

along the life cycle of a product (UNEP and SETAC 2009). S-<strong>LCA</strong> follows four phases, similarly to an (environmental)<br />

<strong>LCA</strong>: goal and scope def<strong>in</strong>ition, <strong>in</strong>ventory analysis, impact assessment and <strong>in</strong>terpr<strong>et</strong>ation; nevertheless<br />

it requires adaptations (Grießhammer, Benoît <strong>et</strong> al. 2006). Go<strong>in</strong>g from data to impact assessment <strong>in</strong><br />

S-<strong>LCA</strong> is still a challenge. UNEP and SETAC (2009) have presented a contribution by provid<strong>in</strong>g a list of 31<br />

subcategories related to 5 stakeholders (workers, consumers, local community, soci<strong>et</strong>y and value cha<strong>in</strong> actors)<br />

that can be either aggregated to impact categories or modelled, through pathways, to endpo<strong>in</strong>ts. Thereafter,<br />

m<strong>et</strong>hodological she<strong>et</strong>s for each of the subcategories were elaborated, <strong>in</strong>clud<strong>in</strong>g def<strong>in</strong>ition, contribution<br />

for the susta<strong>in</strong>able development, unit and even possible data sources (UNEP and SETAC 2010). Some Life<br />

Cycle Impact Assessment m<strong>et</strong>hods, to subcategory level, were also proposed (Dreyer, Hauschild and Schierbeck<br />

(2006); Ciroth and Franze (2011)). The first one is limited to worker stakeholder and the second is not<br />

clear how to evaluate from data to the subcategory and how to aggregate subcategories <strong>in</strong>to impact categories.<br />

The aim of this study is to propose a Subcategory Assessment M<strong>et</strong>hod (SAM) to decrease the variability<br />

of the evaluation of subcategories <strong>in</strong> S-<strong>LCA</strong> studies. A proposal for stakeholder worker and a case study to<br />

test it are presented. SAM <strong>in</strong>cludes 8 subcategories (freedom of association and collective barga<strong>in</strong><strong>in</strong>g, child<br />

labor, fair salary, work<strong>in</strong>g hours, forced labour, equal opportunities/discrim<strong>in</strong>ation, health and saf<strong>et</strong>y, social<br />

benefits/social security) from the stakeholder worker of UNEP and SETAC (2009). SAM enables the analysis<br />

of the organisation <strong>in</strong> four classes (A, B, C and D) for each subcategory. Fulfill<strong>in</strong>g Class A means that the<br />

organisation shows a proactive behaviour compared to the basic requirement. The basic requirement is def<strong>in</strong>ed<br />

for each subcategory, based on International Agreements. Class B means that the organisation follows<br />

the basic requirement. Classes C and D identifies the organisation which does not me<strong>et</strong> the basic requirement<br />

and are differentiated due to generic data which provides background <strong>in</strong>formation concern<strong>in</strong>g the possibility<br />

of the environment to have a positive outlook to social issues. SAM was applied <strong>in</strong> a small w<strong>in</strong>ery to evaluate<br />

stakeholder worker. The case study showed that it was possible to collect data and evaluate a company<br />

us<strong>in</strong>g SAM. Results show that S-<strong>LCA</strong> is as time and work demand<strong>in</strong>g as (environmental) <strong>LCA</strong>, s<strong>in</strong>ce the<br />

issues are specific and change from company to company, sector to sector, and region to region. SAM may<br />

also be implemented for the whole product life cycle. Future development of SAM will <strong>in</strong>clude the other<br />

subcategories, adapt<strong>in</strong>g the basic requirement for each one.<br />

References<br />

Ciroth, A., Franze, J., 2011. <strong>LCA</strong> of an Ecolabeled Notebook – Consideration of Social and Environmental<br />

Impacts along the entire Life Cycle, Berl<strong>in</strong>.<br />

Dreyer, L.C, Hauschild, M., Schierbeck ,J., 2006. A framework for social life cycle impact assessment. Int J<br />

Life Cycle Assess. 11, 2, 88–97.<br />

Grießhammer, R., C. Benoît, <strong>et</strong> al., 2006. Feasibility study: <strong>in</strong>tegration of social aspects <strong>in</strong>to <strong>LCA</strong>. Available<br />

from http://www.saiplatform.org/uploads/Library/UNEP-SETACLifeCycleInitiativeTFonSocialIssues-<br />

FeasibilityStudy.pdf Last visited on 13/01/<strong>2012</strong>.<br />

UNEP and SETAC, 2009. Guidel<strong>in</strong>es for social life cycle assessment of products, United Nations Environment<br />

Program, Paris SETAC Life Cycle Initiative United Nations Environment Programme.<br />

UNEP and SETAC, 2010. Social Life Cycle Assessment: M<strong>et</strong>hodological She<strong>et</strong>s of Sub-Categories of Impact<br />

for Social <strong>LCA</strong>. Available from http://fr1.estis.n<strong>et</strong>/builder/<strong>in</strong>cludes/page.asp?site=lc<strong>in</strong>it&page_id=<br />

D45A9A8F-10FA-4501-BF93-FB9AEAE4D163 Last visited on 23/01/<strong>2012</strong>

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