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Produktlinienanalyse Waschen und Waschmittel (UBA) 1996 ... Biodegradable plastics (VKE, IGBCE, Lower Saxony Environment Ministry) 1999 ... – PowerPoint PPT presentation

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Title: Kein Folientitel


1
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2
PROSA
  • PROSA is a method for the strategic analysis and
    management of product portfolios, products and
    services
  • mainly for companies, but also for product policy
    and dialogue processes
  • gives due regard to time and cost restrictions
  • calls as far as possible on existing tools

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PROSA - case studies
  • Produktlinienanalyse (methodology washing
    insulation) 1986
  • Produktlinienanalyse Waschen und Waschmittel
    (UBA) 1996
  • Sorbic acid preservative (Hoechst AG) 1997
  • PET roofing material (Hoechst AG) 1997
  • Biodegradable plastics (VKE, IGBCE, Lower Saxony
    Environment Ministry) 1999
  • Bt-maize (Novartis AG) 2000
  • 3-Liter-Lupo (Volkswagen AG / BMBF) 2005
  • Virtual answering machine (German Telecom / BMBF
    ) 2003
  • Washing machines (IKW / BMBF) 2005
  • EcoTopTen sustainable products (BMBF) 2005

6
Development of new subtools
  • Social Life Cycle Assessment (SLCA)
  • Life Cycle Costing (partly)
  • Consumer research tool benefit
  • Sustainability Assessment Model proposal ProFitS
    (Products fit to sustainability)

7
Feasibility Study
  • Social LCA is this really feasible?
  • UNEP-SETAC-Life Cycle Initiative, Taskforce
    Integration of social aspects into LCA
  • Launch today Feasibility StudyIntegration of
    social aspects into LCA
  • Rainer Grießhammer, Catherine Benoit, Louise
    Camilla Dreyer, Anna Flysjö, Andreas Manhart,
    Bernard Mazijn, Andreé-Lise Methot and Bo Weidema
    (authors), contributions of further members of
    the taskforce

8
Feasible? Yes, but
  • Abstract...In terms of methodology, there are
    evidently no fundamental problems calling the
    feasibility of SLCA into question. There are
    however certainly considerable hurdles to be
    overcome in practice, especially in
    characterisation modelling, because social
    impacts will require an entirely different type
    of modelling. Hurdles arise in the categorization
    of indicator groups, in the classification of the
    associated individual indicators and in their
    characterization. It is quite probable that the
    very different appraisals of social aspects by
    different actors and in different countries, in
    combination with the process of interdisciplinary
    scientific discourse, will delay agreement for a
    longer time. ....

9
Structure like LCA
  • Goal and scope definition
  • Inventory analysis
  • Impact assessment
  • Interpretation

10
More Priority on Stakeholders
  • More priority on the process and integration of
    stakeholder positions
  • It is wise to include stakeholder or at least
    stakeholder positions (an obligation to integrate
    stakeholders formally would go to far)
    (feasibility study p. 4)

11
More Priority on Functional Equivalence
  • Describe the functional equivalence (technical
    utility) and the corresponding social and
    symbolic functions for the consumer (time
    requirement, convenience, prestige etc.)
  • Social impacts or benefits on the consumer
    should be described as part of the product
    utility (p. 5) and not as social impact along
    the life cycle (!)

12
Inventory analysis typical problems
  • Only a smaller part of the data sought is
    available in processed form from statistical or
    other sources.
  • No module data are yet available for several
    recurrent processes and activities (e.g.
    electronic component manufacturing, cotton
    production, railway use, web-based trading,
    etc.).
  • Several dozen or even hundreds of upstream chains
    can be involved, particularly in the case of more
    complex industrial products (see ongoing study
    PROSA Computer).

13
Indicators
  • There is a need for a structured list of well
    discussed indicators with clear definition
  • It depends on the goal and scope of the case
    studies which indicators are used and whether the
    database is sufficient.
  • Two complementary classification systems
    stakeholder approach (workforce, local community,
    consumers, society) andimpact categories

14
Quantitative and/or qualitative Indicators?
  • The taskforce took side for a combination of
    quantitative and qualitative data, indicators and
    analysis. It voiced the opinion, that
    quantitative data and indicators alone are
    insufficient to cover all aspects of social
    impacts. (p. 8)
  • On the other hand one has the possibility to
    translate qualitative results (e.g. corruption)
    into (semi)quantitative results (p. 8)

15
Next important steps are
  • to establish a generally accepted list of social
    indicators (inventory indicators, midpoint
    indicators, endpoint indicators), structured
    after stakeholder groups and after generally
    accepted impact categories. The connection with
    indicators in the field of CSR (GRI, SA 8000, ILO
    etc.) should be emphasised
  • to define and charakterize the single indicators
    and typical measurement units (p. 13)

16
Impact assessment
  • Classification e.g. jobs (full-time or part-time
    jobs are meant, or minijobs, or jobs created
    under publicly-assisted schemes, self-employed
    jobs, well-paid, poorly paid, secure or insecure
    jobs, jobs within the country studied or abroad)
  • Characterisation e.g. full-time jobs
    (100)1,0part-time jobs (50) 0,5 side-line
    job
  • Optional step Normalization e.g. reduction of
    100.000 t CO2 and 400 jobs being lost in Germany

17
Interpretation
  • General checks (completeness, consistency,
    sensivity)
  • Evaluation process (participation of relevant
    actors, documentation, transparency, conformity
    with the goal of the study )
  • Qualitative evaluation or use of(semi-)quantitati
    ve evaluation models

18
Contact and website
  • Dr. Rainer Grießhammer Öko-Institut e.V.PO Box
    6226, d-79038 Freiburgr.griesshammer_at_oeko.de
  • www.prosa.org
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