An Introduction to Life Cycle Assessment (LCA)
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1 An Introduction to Life Cycle Assessment (LCA) Alissa Kendall, Ph.D. Assistant Professor Civil and Environmental Engineering University of California, Davis Nick Santero, Ph.D. Postdoctoral Scholar Civil and Environmental Engineering University of California, Berkeley
2 Life Cycle Assessment (LCA) A method for characterizing and quantifying environmental sustainability Applies a cradle-to-grave perspective when analyzing products or systems Measures inputs and outputs of a product or system Example inputs: energy, water, materials Example outputs: air emissions, waste Can be categorized into impact categories General standards set by ISO series Provides general LCA guidance, but lacks detailed information necessary for individual products and systems 2
3 Life cycle assessment Evaluates a product or system throughout its entire life cycle M,E M,E M,E M,E M,E Raw Material Acquisition Material Processing Manufacturing Use End-of-Life W, P M = Materials E = Energy W = Waste P = Pollution = Transport W, P Recycle W, P Remanufacture W, P Reuse W, P Recycle 3
4 Let s Simply Define the Life Cycle of an Everyday Object 4
5 Three Key Elements of Life Cycle Assessment Goal Definition and Scope Life Cycle Inventory Assessment Interpretation Impact Assessment Figure based on ISO
6 LCA Standards ISO = International Organization for Standardization ISO LCA Standards: Principles and Framework Requirements and Guidelines Impact Assessment Standards are general guidelines Provides general LCA guidance, but lacks detailed information necessary for individual products and systems 6
7 Three Key Elements of Life Cycle Assessment Key steps include system boundary definition essentially, what can be left out of the LCA? Goal Definition and Scope Life Cycle Inventory Assessment Interpretation Impact Assessment Figure based on ISO
8 Scope Scope of the study function and functional unit system boundaries data requirements/assumptions/limitations Defining the functional unit is an extremely important step In comparative LCA, this will define what products and systems are comparable to one another 8
9 Defining Function & Functional Unit Function service provided by system; performance characteristics of the product Functional unit means for quantifying the product function basis for an LCA reference for normalization of input and output data 9
10 Functional Unit The functional unit also needs to define a timehorizon. A light bulb will likely be defined by the amount of light (lumens) provided (the service/function) for a certain number of hours (the time horizon). The time-horizon is not always hours/days/years A vehicle functional unit could be based on miles driven, years of use, or both 10
11 What are the consequences of a functional unit? When comparing light bulbs (e.g. compact fluorescent and incandescent) you must compare light bulbs with the same luminescence 11
12 What are the consequences of a functional unit? Can you think of any other functions that are different between fluorescent and incandescent lights? 12
13 CFL vs. Incandescent Case Study: Compare a CFL with an output of 900 lumens, and a 10,000 hour life, An incandescent bulb with an output of 900 lumens and 1,000 hour life How many incandescent bulbs are needed to serve a study where the functional unit is 900 lumens delivered for 10,000 hours? 10,000/1,000 = 10 bulbs = 13
14 Why Time Horizon Matters What if we made the study time horizon 11,000 hours? 11 incandescent bulb lifetimes 2 CFL Bulbs (1 bulb, + 10% of the useful life of another) How should we treat the remaining useful life of the CFL? Think about comparing pavement designs One with an expected 32 year lifetime and another with 45-year lifetime? 14
15 Simplified Life Cycle Hg Emissions for CFL and Incandescent Bulbs Why would we do this? CFLs have Hg vapor in their glass tubing. When bulbs are broken, the Hg (in elemental form) is released to the environment. If disposed in a trash bin, breakage is inevitable Our electricity grid in the U.S. emits on average mg Hg/kWh Trade-off: more Hg from electricity vs. Hg emissions at disposal Functional unit: 1700 lumens, 10,000 hours of light. The CFL bulb is a 25 W bulb, the Incandescent is a 100 W bulb. 15
16 Simplified Life Cycle Hg Emissions for CFL and Incandescent Bulbs 5 mg Hg used for production 25W x hr = 250 kwh mg Hg / kwh Electricity * 250 kwh = 4.66 mg Hg ~0 mg Hg ~0 mg Hg 5 mg Hg 9.66 mg Hg Bulb Production Distribution to Retail Home Use End-of-Life Home disposal, Transport, Processing ~0 mg Hg ~0 mg Hg ~0 mg Hg mg Hg 100W x hr = 1000 kwh mg Hg / kwh Electricity * 1000 kwh = mg Hg 16
17 System Boundary Definition The system boundary defines which unit processes and which parts of the life cycle should be included in the study There are situations where unit processes or even life cycle phases could be excluded from an analysis This definition critically effects the outcome of an LCA, and determines whether outcomes of studies can be compared to one another 17
18 Three Key Elements of Life Cycle Assessment Goal Definition and Scope Life Cycle Inventory Assessment Interpretation Impact Assessment Figure based on ISO
19 Life Cycle Inventory (LCI) The accounting stage for LCA Inputs Primary Materials Recycled Materials Primary Energy Land Life Cycle Inventory System Evaluated Outputs Co-Products Air Pollutants Water Effluents Solid Waste 19
20 Data Quality Considerations Many times we rely on existing life cycle inventory datasets, rather than collecting new data Considerations include Age of datasets Are datasets in a study all collected and created with the same methodology? Geography of study vs. geography of data Uncertainty in data 20
21 Where do we get data? Literature Journal papers Research reports Industry data Government data Models General LCA models e.g., Simapro, Gabi, EIO-LCA Product specific models e.g., PaLATE (pavements), BEES (buildings) 21
22 Three Key Elements of Life Cycle Assessment Goal Definition and Scope Life Cycle Inventory Assessment Interpretation Impact Assessment Figure based on ISO
23 Impact Assessment At this stage, the LCI is translated into meaningful metrics and indicators Usually, we create impact categories for climate change, air pollutants, and water effluents Impact is dependent on the fate of pollutants and who or what environments are exposed For our light bulb example, there are big differences in the way Hg is emitted and how people/environments are exposed 23
24 Impact Assessment: Hg from lighting Hg Hg Hg Hg Lake Hg Ingestion CH 3 Hg Inhalation Hg 24
25 Impact assessment: Inputs Input related categories Abiotic resource extraction Biotic resource extraction Fossil energy Total primary energy Water consumption 25
26 Impact assessment: Example Outputs Output related categories global warming potential e.g. convert LCI outputs of GHG emissions using global warming potential to CO 2 e human toxicity e.g. convert toxic pollution recorded in the LCI into its potential or estimated toxicity to humans ecotoxicity photo-oxidant formation acidification nutrification 26
27 Approaches to LCA Process A Process B Process C Process D Process E Process F Process-based Breaks product into individual processes Allows for detailed, specific analyses Necessary to truncate upstream supply chain Input-Output Uses flows between sectors of economy to calculate impact Integrates entire upstream supply chain Uses national averages Necessary to allocate within shared sectors United States: 27
28 Modeling Errors Truncation Error Truncation of the upstream supply chain Process A Process B Process C Process D Process E Process F Allocation Error Necessary to allocate impact when multiple products share common processes Petroleum Refining Bitumen Diesel Gasoline Kerosene Plastics Etc. Bitumen Aggregation Error Assumption that all like products are made using identical processes (averaging) 28
29 Hybrid LCA Combines Process and EIO-LCA approaches Process used for the most critical and unique processes EIO-LCA used for commodity-type processes. Used to model upstream supply chain impacts. Hybrid LCA can reduce modeling errors No truncation error Minimize aggregation and truncation error 29
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