Life Cycle Assessmentjzelek/teaching/syde361/syde361-environment.pdf• Won’t review all of them...
Transcript of Life Cycle Assessmentjzelek/teaching/syde361/syde361-environment.pdf• Won’t review all of them...
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Life Cycle Assessment:
Modified from:
H. Scott Matthews
Civil and Environmental EngineeringCarnegie Mellon University
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Life-Cycle Assessment (LCA)• A concept and methodology to evaluate the environmental effects of
a product or activity holistically, by analyzing the whole life cycle of a particular product, process, or activity (U.S. EPA, 1993).
• LCA studies analyze the environmental aspects and potential impacts throughout a product's life cycle (e.g., cradle-to-grave) from raw material acquisition through production, use and disposal (ISO).
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LCA Uses• Process analysis• Material selection• Product evaluation• Product comparison• Policy-making• Measuring performance• Marketing
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Components of LCA -3 or 4 I’s
• Inventory• Impact Assessment• Interpretation (and Improvement)
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Components and Criteria• Criteria:
– Spatial, Temporal– Design– Functional unit– Significance/magnitude– Uncertainty
• ISO documents a framework (not a recipe); LCAs may or may not consider all points above
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Criticisms / Limitations• Data reliability and quality is questionable.• Models based on assumptions.• Problem boundaries are arbitrary. • Scale issues - global -> local, etc.• Uncertainty is everywhere• Spatial and temporal issues• Comparisons between studies difficult• No single, accepted method
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Important Note on Context• LCA should be one part of a broad
environmental assessment• If comparing with LCA, all assumptions
and methods should be consistent– Especially problematic for validating
against external studies
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Definitions• Big set of definitions in ISO framework
documents (e.g., p.1 of ISO 14040)• Won’t review all of them here, but you
need to know them.• Big ones to know are unit process,
elementary flows, inputs, outputs
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Definitions• Elementary flows - material or energy
entering or leaving the system, directly to/from the environment, without human transformation
• Unit process - smallest portion of a product being studied for which LCI data available
• Inputs / Outputs - materials or energy entering or leaving a unit process
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Scope Considerations• Setting all the parameters for study
– e.g., functional unit, boundaries, data, etc.– Whether it will be critically reviewed
• May be iterative (update in progress)• Supports product system diagram
– Realize LCA can be used for ‘products’, ‘processes’, ‘systems’, etc.
• Functional unit definition ensures unit consistency for validation and comparison
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Product Systems• Collections of unit processes, elementary
flows, and product flows• Also shows system boundary• Processes, flows maybe in / out of bounds
– In: fuel, energy, materials, …– Out: emissions, waste, …
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Simple Example - Tree
SunlightCO2
O2
Wood
Environ- ment
Tree EnergySystem?Water
If we wanted to do a life cycle inventory of a tree, we could draw the boundary in one of several places
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More Complex Example• We manufacture a part for new
automobiles and ship it in cardboard boxes
• Currently, we “ship and forget it”• Generates significant box waste• We want to reduce waste - how?• What are tradeoffs?
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Original System
ManufactureSystem Packaging Transport/
Delivery
Energy
Emissions, Cardboard Box Waste
Car Assembly
Part
Energy
Cardboard Manuf.
UnboxedPart
Raw Mats, Energy
Emissions,Waste
BoxedPart
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Packaging Takeback System
Manuf.System
PartPackaging
Transport/Delivery
Emissions, (Less?) Cardboard Waste
Car Assembly
Cardboard Manuf.
Unboxed Part
Empty Box
Transp/Logistics
Reused Box
Energy
Emissions
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Packaging Takeback System• Our new system uses less cardboard
– Thus less waste, manufacturing impacts• But uses more transportation to retrieve used
boxes– Thus more energy use, emissions
• Unclear whether this tradeoff is beneficial• Perfect application for LCI/LCA
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Example Goal/Scope• Goal: “To determine whether the new system is
better than the old” – More detail: which inventory items? How to assess?– Maybe air emissions, energy use, waste generated– Would a better goal originally have been to do LCA of
old system and suggest improvements?• Scope: Fairly detailed description of both
systems, items in/out of boundaries– e.g., might exclude impacts of product (relevant?)– But include packaging/logistics/reuse of systems
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Next Step: Inventory• In general, just “good research”• “Look up the data, add it up”
– However, data availability varies widely• Consider inputs, outputs of interest
– In: energy, resources, etc.– Out: emissions, waste, etc.
• Also may be iterative• Allocation an issue
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Inventory Process• Iterative• Collect/validate• Matching data with
unit processes/ functional units/etc
• See “sample forms” on pp.16-20 of ISO 14041 PDF.
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Allocation• Hard to assign “one to one” linkages between
units and inputs-outputs• Need standard/specified way to distribute
(allocate) them– mass balance method– Physical properties– Economic value ratio?
• What allocations needed for packaging takeback system?
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Inventory Interpretation• How do results fit goal/scope?• Assessment of data quality• Sensitivity analysis on inputs/outputs
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Impact Assessment
• Classification• Characterization• Weighting (e.g. taking an inventory of
various toxics, then weighted by toxicity)– Assumed that existing weighting methods
can be used (not developed as part of LCA)
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Resources• http://www.eiolca.net - tutorial on-line
• Don’t despair, you do not need to collect all of your own data for LCAs, for example:– US NREL LCI Database (various): http://
www.nrel.gov/lci/– BEES (construction materials): http://
www.bfrl.nist.gov/oae/software/bees.html
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Check out book:• Environmental Life Cycle
Assessment of Goods and Services: An Input-Output Approach (RFF Press) (Paperback) by Chris T. Hendrickson (Author), Lester B. Lave (Author), H. Scott Matthews; 2006