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Impact Assessment and Interpretation in LCA H. Scott Matthews Research Director, Green Design Institute Associate Professor, Civil and Environmental Engineering / Engineering and Public Policy
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Eco-indicator 99 method Note TRACI is conceptually similar 3 categories of endpoints: –Human Health –Ecosystem quality –Resources Damages to human health expressed as disability adjusted life years (DALYs) Damages to ecosystems expressed as percent of species lost due to env’l loading Resource constraints expressed as function of remaining reserves
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Cultural Theory Model Due to uncertainties, contains embedded assumptions to make 3 damage models –Egalitarian (long term, minimal sci. evidence) –Individualist (short term, only believes proven) –Hierarchist (balanced, wants consensus)
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Using DALYs Carcinogens cause some deaths per yr Death has disability rating of 1 If a type of cancer shortens life by 10 years, we say it has value of 10 DALYs –Ex: during summer smog, people treated in hospital. Treatment has rating of 0.4 on DALY scale. –If treatment lasts 0.01 yrs, each case could be weighted as 0.004 DALYs
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Notes Ecosystem and resource factors work in a similar way (weights) Do the example on the board using the handout of eco-indicator weights for health effects only. –First, can you verify the numbers in the 2 columns of each table? –Then do your weightings..
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Interpretation Inventory + Impact combined Make results fit within goal and scope Double check model and analyze results Conclusions + Recommendations –e.g., “use phase/certain process is most important” Maybe iterative re-goal/re-scope based on preliminary findings –E.g. “we didn’t realize certain material would be 95% of results - need to do more to understand that material in scope”
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Sample Interpretation Results Can also display as category percents -> materials prod significant
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Sample Interpretation Results Similar but now grouped by processes -> Energy significant
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Sample Sensitivity Analysis The 2 allocation methods suggest that you cannot really differentiate Between Options A and B.
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Extended Producer Product Responsibility (EPR) or “Aiming towards Closed- Loop Supply Chains”
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EPR in US Safety – labeling and potential liability –Children choking on toys –Laptops overheating Malfunction – warranties Leasing/Services as marketing opportunity –Copying machines –Vehicles (airplanes, railcars, automobiles) –Solvents –Carpet
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EPR in US(cont.) Batteries: legislated return programs –Lead acid battery deposits and restrictions –Rechargeable battery recycling act (big issue – use of post to send batteries) Recycling encouragement programs –Aluminum –Steel –Motor vehicles –Computers
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European EPR Voluntary agreements for product takeback: automobiles, electronic products, packaging Industry sponsored disassembly and recycling operations
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Example: European Power Tools Mfg. agreement to support takeback and recycling of power tools. Collection at retail stores, ship in bulk to recycling center, repair or shredding. Recycling loses money for each power tool (shipping + handling > material sale) –charges to mfg of power tool. –Charges roughly equal reverse logistics costs.
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Power Tools (cont.) Relatively few power tools returned –Lack of incentive to return. –Pile up in attics, basements, garages, etc. –Export of used tools to Eastern Europe Re-manufacturing possibility – Markus Klausner –Re-manufacturing more profitable than recycle: return a rebate for returns –Re-manufacturing depends upon motor
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Datalogger Device inserted into power tool to record use and temperature. Read-out to aid re-manufacturing decision making Ancillary use – effective way to gather information on actual power tool use.
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BOSCH Datalogger
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Datalogger (cont.) Cost of datalogger incurred for all power tools. Profit only for returned power tools suitable for re-manufacturing Wish to Encourage More Returns
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Design for End-of-Life Easier disassembly Information on materials – on product or in database? Limited number of materials Valuable materials – reduce life cycle cost? Mfg. Incentive for DfE-o-L?
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Electronics Packaging Takeback From earlier Lecture, how to organize system for cost/environment? Current system “ships and forgets” Leads to significant packaging waste How can system be redesigned? What are tradeoffs? See Matthews California Management Review, 2004 paper (given out in class)
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Packaging Takeback System Manuf. System Part Packaging Transport/ Delivery Emissions, (Less?) Cardboard Waste Computer Assembly Cardboard Manuf. Unboxed Part Empty Box Transp/ Logistics Reused Box Energy Emissions
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LCI and Accounting Life Cycle Inventories are inherently accounts of effects as estimated As discussed earlier, using and interpreting inventories a challenge This is major current research area Only limited useful results (we’ll see)
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Vectors to Scalars Converting an inventory of even similar effects (e.g. air pollution) into some common unit is difficult It makes sense to understand how the accounting world works and pursues similar issues Also to put in context environmental cost accounting and see how LCA can inform those efforts
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Application of Valuation: Hybrid Electric Vehicles (HEV) ICE and Battery Powered Emissions and Fuel Economy Benefits Toyota Prius - Performance not comparable to current internal combustion engine (ICE) vehicle Evaluate benefits of improved performance Prius and Corolla ICE- Consumer and Social Perspectives
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Hybrid Electric Vehicles Compare lifetime private and social costs of Prius and Corolla Private Costs –Vehicle purchase price –Maint. cost (battery replacement) –Fuel cost Social Costs –Costs of air pollutants and GHG emitted
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Hybrid Electric Vehicles Cost-effective means to achieve emissions reductions? Construct scenarios to equate lifetime costs of Prius and Corolla –HEV price premium –Required gasoline price –Valuation of emissions reductions –Social value of abating carbon dioxide –Note data/assumptions from 2000 (may be different now)
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Hybrid Electric Vehicles Current Prius or Performance Prius is more costly than the fuel savings, air pollutant and CO 2 emissions benefits would justify To be attractive economically, an HEV will have to offer features that cannot be offered by a conventional ICE
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Conclusions Although controversial.. –Valuation/weighting methods are helpful in collapsing information into meaningful comparisons The types of comparisons possible are large with such methods The number of interesting policy problems to address is large
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Resources We have GaBi license Obviously, EIO-LCA Lester Lave on ed. Board of IJLCA –I have journal issues in my office Journal of Industrial Ecology - editor EPA: –http://www.epa.gov/ORD/NRMRL/lcaccess/resources.htm
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LCA Examples
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LCA of American Cars
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LEED Green Building Standard LEED standard all but begs you to do LCA to get credit points
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LCA: Organic Foods Mixed - what would you expect?
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Recycling MSW
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