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Early Replacement of Notebooks Considering
   Environmental Impacts
- Study commissioned by the German Federal Environment Agency (UBA)




Siddharth Prakash, Öko-Institut e.V.
Ran Liu, Öko-Institut e.V.
Dr. Lutz Stobbe, IZM
Karsten Schischke, IZM

Electronics Goes Green 2012, Berlin
12.09.2012
Content
- Introduction Öko-Institut (Institute for Applied Ecology)
- Background
- Objectives
- Methodology
- Results
- Conclusions
About Öko-Institut e.V.

 Öko-Institut is a leading European research and consultancy
  institute working for a sustainable future.
 Founded in 1977, non-profit association
 More than 130 staff, including 85 researchers
 Offices in Freiburg, Darmstadt and Berlin




                                                                3
About Öko-Institut e.V.
   Clients: European Union, ministries, industrial companies, non-
    governmental organizations
   Annual turnover: some 12 million Euros

Our Issues
 Energy and Climate Protection
 Nuclear Engineering and Facility Safety
 Sustainability in Consumption, Mobility, Resource Management and
  Industry
 Law, Policy and Governance
 Emission and Ambient Pollution Control
 Chemicals Management and Technology Assessment
 Agriculture and Biodiversity




                                                                      4
Background
  Production of notebooks is highly material and energy intensive
  Empirical evidence suggests that actual life-time of notebooks is getting shorter
    Public authorities and private consumers lack information on the
    ecologically optimum time period for the replacement of notebooks
 Wide variations in the life-cycle assessment of notebooks




                 Figure 1: Global Warming Potential (CO2e) in the production phase of selected notebooks
Background
    - UBA R&D Project UFOPLAN (2009): Creation of a database for
    determination of the environmental impacts of ICT products

     No. Dataset name in ProBas     Reference         Notes
                                    unit
     1.   Display module production 1 TFT LCD         With upstream chains
                                    module
     2.   Silicon wafer production   1 cm2 polished   Partly with upstream chains. The upstream
                                     silicon wafer    chains of hydrogen chloride, graphite and
                                                      electrical energy are not included

     3.   IC fabrication front-end   1 cm2 finished   Without upstream chain. However, the
          process  “wafer out”      wafer out        additional input factors for the production of
                                                      high-purity process chemicals are
                                                      characterised.

     4.   IC fabrication front-end   1 cm2 defect-    Without upstream chain. However, the
          process  “good die out”   free die out     additional input factors for the production of
                                                      high-purity process chemicals are
                                                      characterised.

     5.   IC fabrication back-end    1 memory IC      Without upstream chain
          process
Objectives


What is the share of different life cycle phases in the total greenhouse gas
emissions of a notebook?

When are the environmental impacts, which are associated with the production,
distribution and disposal of a new notebook, compensated as a result of energy
efficiency gains in the use-phase of the new notebook?

Which energy efficiency gains should be possessed by a new notebook, if the
replacement of the older and less energy efficient notebook can be justified under
the consideration of environmental concerns?
Methodology
- Measurement of greenhouse gas emissions of a notebook on the
basis of three different data sources
-   EuP Lot 3
-   EcoInvent 2.2
-   UBA R&D Project, UFOPLAN 2009
Methodology


Function und functional unit – 1 Notebook with a life-time of 5 years




 Goal of the study was not to produce a comparative LCA of different notebooks
 The procedure adopted for this LCA study still follows ISO 14040/44, but only
  examines one impact category, namely Global Warming Potential (GWP)
Methodology
Use Phase based on data bank of Energy Star Version 5.0 for Computers
Methodology
End-Of-Life
-EcoInvent 2.2 - „Disposal, Laptop Computer, in E-Scrap-Processing“

-BUSINESS-AS-USUAL




  -BEST PRACTICE
Methodology
End-Of-Life

-EcoInvent 2.2 - „Disposal, Laptop Computer, in E-Scrap-Processing“




                                                              360 mg

                                                              240 mg
                                                                       24 mg
Methodology
Amortisation calculation
- Assumptions
     - New notebook more energy efficient than the old notebook
     - Energy efficiency improvements of the new notebooks in 10% intervals
       (10%, 20%, 30%.........70%)
     - Measurement of the saving potential of the new notebook




     Amortisation time:
Results
 Absolute GWP emissions outcome for all scenarios studied
 (kg CO2e/notebook)
Results
 Amortisation period as a function of energy efficiency
 improvement in the use phase
Results
  Sensitivity Analysis: Significance of life-time




Manufacturing phase contributes towards 76% of the total greenhouse gas
emissions of a notebook, if the life-time is reduced to 2,9 years




                                                                    16
Results
  Sensitivity Analysis: Use phase according to EuP Lot 3




Manufacturing phase contributes towards 46% of the total greenhouse gas
emissions of a notebook, if use phase is modelled according to EuP Lot 3




                                                                     17
Conclusions
Recycling: Low concentration of selected metals (Au, Ag and Pd) in Notebooks leads to a small reduction
potential of 3 kg CO2e per Notebook between Best-Practice und Business-as-Usual Scenario

Recycling: If recovery of a larger group of metals is considered, the reduction potential of greenhousegas
emissions would be much higher, and, if other environmental impacts, such as acidification and
eutrophication potential, are considered, reduction in the total environmental burden is more visible.

Production: The share of production phase is lowest with EuP Lot 3 (81 kg CO2e; 35,2%) and highest
with the data source of UBA R&D project (216 kg CO2e; 56%)

Production: Production of the Motherboard causes 70 to 85 kg CO2e;
            Production of the display module causes 35 to 41 kg CO2e


Use: Even if the energy consumption in the use-phase is doubled, environmental burden of
production phase is quite substantial.


The MEEuP-method used within the framework of ecodesign directive underestimates the
environmental burden of the production of electronic components

Extension of life-time of a notebook reduces the contribution of production phase towards total
greenhouse gas emissions of a notebook
Conclusions

Proceeding from an assumed lifetime of 5 years, this means that a replacement of the notebook only
pays in environmental terms if the EuP Lot 3 data are used, but even then only if energy efficiency is
improved by 70%. Such an efficiency improvement between two notebook generations of similar
configuration and functionality is unrealistic.



If we assume a realistic energy efficiency improvement of 10% between two notebook generations,
the amortisation periods are between 33 and 88 years, while if energy efficiency improves by 20%
the period is between 17 and 44 years, depending upon the data source used to analyse notebook
production. Evidently no notebook has such a useful lifetime.



Amortisation calculation: The analysis of environmental amortisation periods has shown that the
environmental impact associated with the production of a notebook is so great that it cannot be
compensated in a realistic period of time by its improved energy efficiency during the use phase
– regardless of which data source is used.

It therefore follows from this study that it is not environmentally purposeful (with regard to global
warming potential) to purchase a new notebook after a period of only a few years, even if the
assumed energy efficiency of the new device exploits the full scope of cutting-edge technology.
Conclusions


 Focus of product design for ICT devices should be placed on
   the aspects that lead to an extension of device lifetimes
     Possibilities of hardware upgrading
     Modular construction
     Recycling-friendly design
     Availability of spare parts
     Standardisation of components
     Extension of minimum warranty periods




                                                               20
Thank you very much for your attention!
Contact Details:
Siddharth Prakash
Sustainable Products & Material Flows
Öko-Institut
Tel: +49-761-45295-244
E-Mail: s.prakash@oeko.de

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Early Replacement of Notebooks Considering Environmental Impacts

  • 1. Early Replacement of Notebooks Considering Environmental Impacts - Study commissioned by the German Federal Environment Agency (UBA) Siddharth Prakash, Öko-Institut e.V. Ran Liu, Öko-Institut e.V. Dr. Lutz Stobbe, IZM Karsten Schischke, IZM Electronics Goes Green 2012, Berlin 12.09.2012
  • 2. Content - Introduction Öko-Institut (Institute for Applied Ecology) - Background - Objectives - Methodology - Results - Conclusions
  • 3. About Öko-Institut e.V.  Öko-Institut is a leading European research and consultancy institute working for a sustainable future.  Founded in 1977, non-profit association  More than 130 staff, including 85 researchers  Offices in Freiburg, Darmstadt and Berlin 3
  • 4. About Öko-Institut e.V.  Clients: European Union, ministries, industrial companies, non- governmental organizations  Annual turnover: some 12 million Euros Our Issues  Energy and Climate Protection  Nuclear Engineering and Facility Safety  Sustainability in Consumption, Mobility, Resource Management and Industry  Law, Policy and Governance  Emission and Ambient Pollution Control  Chemicals Management and Technology Assessment  Agriculture and Biodiversity 4
  • 5. Background  Production of notebooks is highly material and energy intensive  Empirical evidence suggests that actual life-time of notebooks is getting shorter Public authorities and private consumers lack information on the ecologically optimum time period for the replacement of notebooks  Wide variations in the life-cycle assessment of notebooks Figure 1: Global Warming Potential (CO2e) in the production phase of selected notebooks
  • 6. Background - UBA R&D Project UFOPLAN (2009): Creation of a database for determination of the environmental impacts of ICT products No. Dataset name in ProBas Reference Notes unit 1. Display module production 1 TFT LCD With upstream chains module 2. Silicon wafer production 1 cm2 polished Partly with upstream chains. The upstream silicon wafer chains of hydrogen chloride, graphite and electrical energy are not included 3. IC fabrication front-end 1 cm2 finished Without upstream chain. However, the process “wafer out” wafer out additional input factors for the production of high-purity process chemicals are characterised. 4. IC fabrication front-end 1 cm2 defect- Without upstream chain. However, the process “good die out” free die out additional input factors for the production of high-purity process chemicals are characterised. 5. IC fabrication back-end 1 memory IC Without upstream chain process
  • 7. Objectives What is the share of different life cycle phases in the total greenhouse gas emissions of a notebook? When are the environmental impacts, which are associated with the production, distribution and disposal of a new notebook, compensated as a result of energy efficiency gains in the use-phase of the new notebook? Which energy efficiency gains should be possessed by a new notebook, if the replacement of the older and less energy efficient notebook can be justified under the consideration of environmental concerns?
  • 8. Methodology - Measurement of greenhouse gas emissions of a notebook on the basis of three different data sources - EuP Lot 3 - EcoInvent 2.2 - UBA R&D Project, UFOPLAN 2009
  • 9. Methodology Function und functional unit – 1 Notebook with a life-time of 5 years  Goal of the study was not to produce a comparative LCA of different notebooks  The procedure adopted for this LCA study still follows ISO 14040/44, but only examines one impact category, namely Global Warming Potential (GWP)
  • 10. Methodology Use Phase based on data bank of Energy Star Version 5.0 for Computers
  • 11. Methodology End-Of-Life -EcoInvent 2.2 - „Disposal, Laptop Computer, in E-Scrap-Processing“ -BUSINESS-AS-USUAL -BEST PRACTICE
  • 12. Methodology End-Of-Life -EcoInvent 2.2 - „Disposal, Laptop Computer, in E-Scrap-Processing“ 360 mg 240 mg 24 mg
  • 13. Methodology Amortisation calculation - Assumptions - New notebook more energy efficient than the old notebook - Energy efficiency improvements of the new notebooks in 10% intervals (10%, 20%, 30%.........70%) - Measurement of the saving potential of the new notebook Amortisation time:
  • 14. Results Absolute GWP emissions outcome for all scenarios studied (kg CO2e/notebook)
  • 15. Results Amortisation period as a function of energy efficiency improvement in the use phase
  • 16. Results Sensitivity Analysis: Significance of life-time Manufacturing phase contributes towards 76% of the total greenhouse gas emissions of a notebook, if the life-time is reduced to 2,9 years 16
  • 17. Results Sensitivity Analysis: Use phase according to EuP Lot 3 Manufacturing phase contributes towards 46% of the total greenhouse gas emissions of a notebook, if use phase is modelled according to EuP Lot 3 17
  • 18. Conclusions Recycling: Low concentration of selected metals (Au, Ag and Pd) in Notebooks leads to a small reduction potential of 3 kg CO2e per Notebook between Best-Practice und Business-as-Usual Scenario Recycling: If recovery of a larger group of metals is considered, the reduction potential of greenhousegas emissions would be much higher, and, if other environmental impacts, such as acidification and eutrophication potential, are considered, reduction in the total environmental burden is more visible. Production: The share of production phase is lowest with EuP Lot 3 (81 kg CO2e; 35,2%) and highest with the data source of UBA R&D project (216 kg CO2e; 56%) Production: Production of the Motherboard causes 70 to 85 kg CO2e; Production of the display module causes 35 to 41 kg CO2e Use: Even if the energy consumption in the use-phase is doubled, environmental burden of production phase is quite substantial. The MEEuP-method used within the framework of ecodesign directive underestimates the environmental burden of the production of electronic components Extension of life-time of a notebook reduces the contribution of production phase towards total greenhouse gas emissions of a notebook
  • 19. Conclusions Proceeding from an assumed lifetime of 5 years, this means that a replacement of the notebook only pays in environmental terms if the EuP Lot 3 data are used, but even then only if energy efficiency is improved by 70%. Such an efficiency improvement between two notebook generations of similar configuration and functionality is unrealistic. If we assume a realistic energy efficiency improvement of 10% between two notebook generations, the amortisation periods are between 33 and 88 years, while if energy efficiency improves by 20% the period is between 17 and 44 years, depending upon the data source used to analyse notebook production. Evidently no notebook has such a useful lifetime. Amortisation calculation: The analysis of environmental amortisation periods has shown that the environmental impact associated with the production of a notebook is so great that it cannot be compensated in a realistic period of time by its improved energy efficiency during the use phase – regardless of which data source is used. It therefore follows from this study that it is not environmentally purposeful (with regard to global warming potential) to purchase a new notebook after a period of only a few years, even if the assumed energy efficiency of the new device exploits the full scope of cutting-edge technology.
  • 20. Conclusions Focus of product design for ICT devices should be placed on the aspects that lead to an extension of device lifetimes  Possibilities of hardware upgrading  Modular construction  Recycling-friendly design  Availability of spare parts  Standardisation of components  Extension of minimum warranty periods 20
  • 21. Thank you very much for your attention! Contact Details: Siddharth Prakash Sustainable Products & Material Flows Öko-Institut Tel: +49-761-45295-244 E-Mail: s.prakash@oeko.de