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Integrating LCIA and LCM:

Integrating LCIA and LCM:. Evaluating environmental performances for supply chain management. Alan Brent Chair: Life Cycle Engineering Department of Engineering and Technology Management University of Pretoria Tel: +27 12 420 3929 Fax:+27 12 362 5307 E-mail: abrent@eng.up.ac.za.

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Integrating LCIA and LCM:

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  1. Integrating LCIA and LCM: Evaluating environmental performances for supply chain management Alan Brent • Chair: Life Cycle Engineering • Department of Engineering and Technology Management • University of Pretoria • Tel: +27 12 420 3929 • Fax:+27 12 362 5307 • E-mail: abrent@eng.up.ac.za

  2. Foundations of LCE at UP Engineering and Technology Management Provincial government initiatives / support Business school Automotive / manufacturing industry LCM & SHE Decision support

  3. Integration of the LCE activities in the Automotive Focus Group (AFG) of UP Chair in Life Cycle Engineering AFG Chair in Automotive Manufacturing Chair in Automotive Engineering Total engineering and management support of the SA automotive industry

  4. The automotive industry as a major exporter of South African products Components Vehicles

  5. The main destinations of the component exports Component manufacturers • 74 % to Europe (46 % to Germany) • 10 % to North America • Catalytic converters (26.6 %) • Stitched leather seat covers (19.5 %) • Tyres (6.6 %) • Exhaust systems (6.2 %) • Wheels (mostly aluminium) (5.4 %)

  6. Future trends in the responsibility of industry Industry's Responsibility Present Challenges: Product Take Back Regulations, Recycling, Work place Product Use Product Retirement Product Manufacturing Tomorrow Future Challenges: Life Cycle Engineering Obligations, Recyclability (waste) and Climate Protection Declarations Work place (new age) Today Yesterday Environment Protection Environment Protection Less Landfill Disposal Economic Efficiency Remanufacturing Less Incineration Reprocessing Organization Performance Technology Endurance Costs

  7. Incorporating sustainable development concepts into management practices Development that meets the needs of the present without compromising the ability of future generations to meet their own needs Economic considerations Business management incorporation Social considerations Sustainable development Environmental considerations Adopting business strategies and activities that meet the needs of the business and its stakeholders today while protecting, sustaining and enhancing the human and natural resources that will be needed in the future

  8. Three life cycles that are fundamental to management in the manufacturing industry Pre-feasibility Feasibility Development Executing & testing Project launch & PIR Pre-manufacture Operation & manufacture Product usage Product disposal Detailed design Commission Operation & Maintenance De-commission • Project life cycles – drivers of internal change • Asset life cycles – optimise internal operations • Product life cycles – profit generation of operations

  9. Pre-feasibility Feasibility Develop Execute & testing Launch Pre-manufacture Commission Operation & Maintenance De-commission Product usage Product disposal Detailed design Project life cycle Asset life cycle Product life cycle

  10. Application of the LCE approach for different management requirements Product Asset Maintenance X Life Cycle Management Project Investment Waste

  11. Sustainable supply management within the integrated Life Cycle Management approach • Integrating with existing management practices • Environmental management • Quality management • Logistics management • Procurement management • Maintenance management • Understanding the value/burden addition of suppliers • Added economic value • Added environmental burdens • Social? Pre-manufacture Operation & Maintenance

  12. Accumulated value and burdens of manufactured products (environmental burdens example) Total burden Internal manufacturing burden External manufacturing burden Suppliers Suppliers First- tier Second-tier Facility

  13. Sustainable supply chain management therefore focuses on environmental performances Total burden Internal manufacturing burden External manufacturing burden Suppliers Suppliers First- tier Second-tier Facility

  14. Problems with assessing environmental performances (from an OEMs perspective in SA) • Lack of detailed environmental data in developing countries • Precise environmental impact causes can not be determined • Smaller supplying countries in developing countries have only limited process information • Only certain process information is currently (systematically) obtained by OEMs in South Africa • Water usage • Energy usage • Waste produced (for land filling) • Comparing environmental performances • Valuated comparisons from an OEMs perspective True reflection of environmental burdens in the South African context

  15. Assessing environmental performances from limited process parameters Water usage ? Determining environmental impacts Environmental performance in the SA context Energy usage Waste produced

  16. Assessing environmental performances from limited process parameters (using ISO 14040) SA-specific LCI SA-specific LCIA Water usage Water resources Water extraction Electricity Air resources Environmental performance in the SA context Raw materials Energy usage Steam (on-site) Land resources Liquid fuel Waste produced Mined abiotic resources Med.-classified

  17. Assessing environmental performances from limited process parameters (SA-specific LCIA) Midpoint cat. Resource groups Water Use Eutroph. Pot. Water usage Water resources Acidif. Pot. POCP Air resources Environmental performance in the SA context ODP Energy usage GWP Land resources HTP ETP Waste produced Mined abiotic resources Land Use Mineral Depl. Energy Depl.

  18. The impacts on the resource groups must reflect the variance in the SA eco-regions

  19. Introduced SALCA Regions for impact assessment of natural resource groups

  20. Environmental resources data compiled for these SALCA Regions • Water quality and quantity • Measurement data of key pollutants • Metals, organics, sulphates, etc. • Maximum yield and usage • Regional and global air impacts • Ambient measurement data in major metropolitan areas • CO2 and CFC-11 measurement data (all regions) • Land quality and quantity • Measurement data of key pollutants • Metals, phosphates, etc. • National land cover database • Land uses, types, etc. • Mined abiotic resources • Platinum reserves (national level) • Coal reserves (national level) Ambient targets to protect resources, human health and ecosystems

  21. Calculation of Resource Impact Indicators (per unit of process parameters RIIG = Resource Impact Indicator calculated for a main resource group through the summation of all impact pathways of LCI constituents QX = Quantity release to or abstraction from a resource of life cycle constituent X of a LCI system in an impact category C CC = Characterisation factor for an impact category (of constituent X) within the pathway NC = Normalisation factor for the impact category based on the ambient environmental quantity and quality objectives, i.e. the inverse of the target state of the impact category SC = Significance (or relative importance) of the impact category in a resource group based on the distance-to-target method, i.e. current ambient state divided by the target ambient state

  22. Normalisation of RII performances of companies with economic value of products (to OEMs) Water Air Land Mined abiotic Water Air Land Mined abiotic Normalisation with economic values of products (to OEMs)

  23. Case study: Process parameters obtained from a South African OEM’s first-tier suppliers Fuel tanka Windscreena Tyrea • Energy usage • Electricity MJ • Liquid fuel (diesel) kg • Steam kg • Raw materials kg 63.7 0.0 0.0 0.0 60.5 0.0 0.0 2.0b 234.1 0.0 20.4 0.0 Water usage kg 4.6 176.8 20.5 Waste produced kg 0.1 32.0 1.0c Economic valued R 1000.00 1460.00 500.00 a Process parameters are shown per supplied component b Natural gas for furnace operation c 10% assumed losses d 9 South African Rand is equal to approximately 1 Euro (€)

  24. RII values calculated per supplied component Fuel tanka Windscreena Tyrea Water resources 2.882×10-1 2.779×10-1 1.067×100 Air resources 6.535×10-3 6.206×10-3 2.406×10-2 Land resources 6.148×10-5 6.113×10-5 2.271×10-4 Mined abiotic resources 3.222×10-5 4.051×10-5 1.271×10-4

  25. RII values calculated per supplied component (per economic value or South African Rand)

  26. Conclusions from the case study • The supplied tyre has the highest overall environmental burden per Rand value • In the order of a factor of 10 compared to the fuel tank and windscreen • However, a supplied tyre has an economic value of half to a third compared with the fuel tank and windscreen • The ratio difference between environmental burdens associated with the complete components would therefore be smaller • Converselyfive tyres are supplied per manufactured automobile, which would increase the environmental burdens (and total cost to the supplier) by a factor of five • For the specific studied sedan • But, only the manufacturing processes of the first-tier suppliers were investigated and compared • Environmental performances of second- and subsequent tiers are required for an overall product evaluation

  27. Determining an overall Environmental Performance Resource Impact Indicator (EPRII) Decision analysis procedures weighting Water resources Air resources Land resources Mined resources

  28. Analytical Hierarchy Procedure (AHP) to determine weighting factors for the resource groups Extremely more important Strongly more important Strongly more important Extremely more important Equally important Importance Importance Criterion 1 Criterion 2 Air Water Air Land Air Abiotic Water Land Water Abiotic Land Abiotic

  29. AHP survey results and national government expenditure trends on the natural resource groups Fraction of national expenditure allocated to environmental issues Distribution of relative weighting values obtained from individual judgements Mean (geometric) relative weighting value obtained for the environmental criteria

  30. Hypothetical overall EPRII for a supplier based on a comparison with another supplier (baseline) -1 0 1 Water resources +1  ww (0.45) -1  wa (0.20) Air resources EPRII Land resources +1  wl (0.25) Mined abiotic resources 0  wm (0.10)

  31. Incorporating sustainable development concepts into management practices Development that meets the needs of the present without compromising the ability of future generations to meet their own needs1 Economic considerations Business management incorporation Social considerations Sustainable development Environmental considerations Adopting business strategies and activities that meet the needs of the business and its stakeholders today while protecting, sustaining and enhancing the human and natural resources that will be needed in the future2

  32. South African on-going LCM activities Closure and questions

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