Life Cycle Assessment Notes
LCA Process
Four main processes:
Scope and definition
Inventory analysis
Impact assessment
Interpretation of results
Goal Definition
Define the objective of the study.
Determine the starting and ending points of the process.
Define the methods to be used.
Identify parameters to be measured.
Scope Definition
Define the boundaries of the study.
Example: Carbon Nanotube (CNT) synthesis:
Base plastic material collection
Shredding
Pretreatment (may or may not be needed)
Chemical Vapor Deposition (CVD) synthesis
Post-treatment (chemical or heat)
Inventory Analysis
LCA studies are data-driven.
Data is required for each step of the process.
Data sources:
Literature
Databases
Experimental work
Assumptions may be necessary
Data Collection
Collect data relevant to the defined scope.
Make necessary assumptions.
Source data from:
Literature
Databases
Government research
International agencies (IEA, UN, etc.)
Assess the authenticity and reliability of data.
Data Preference
Primary data (collected directly from industries/factories) is more valuable and improves accuracy.
Secondary data (from literature) is often used due to the difficulty of obtaining primary data.
Experimental data is also used.
Data Compilation
Split data based on the defined scope and steps.
Collect inventory data from start to end.
Identify data requirements for each step.
Impact Assessment
Calculation based on inventory data.
Can be done using software or manual calculations.
Data needs to be in a standard, normalized unit.
Climate Change Example:
Caused by gases like carbon dioxide, methane, nitrous oxide (), water vapor, and hydrofluorocarbons.
Quantified into a single unit for comparison.
Impact Categories:
Global Warming Potential (GWP)
Acidification Potential
Ozone Depletion Potential
Human Toxicity
Eutrophication
Auto Oxidation Potential
Solid Waste
Ecotoxicity
Data from inventory is converted using conversion and emission factors.
Global Warming Potential (GWP) Example:
Represented as kilogram carbon dioxide equivalent ( equivalent).
Methane conversion factor: 21
Nitrous oxide conversion factor: 310-320
Calculations are compiled (e.g., in Excel).
Interpretation of Results
Compare results with previous literature.
Interpret whether results are favorable.
Analyze why results are higher or lower than expected.
Identify the safest or best pathway for material production.
This stage defines the outcome and objective of the study.
Iterative Process
Life Cycle Assessment is an iterative process.
The arrows in the diagram are double-sided, indicating that the process can go back and forth between stages.
Interpretation of results is connected to all three parameters (scope, inventory, impact assessment).
Accuracy depends on the authenticity of data.
System Boundary
Defines the scope: from start to end of the project.
Cradle-to-gate approach: from raw material extraction to the factory gate.
Factory gate: point before retailer, wholesaler, or final consumer.
Example of CNTs: sourced from plastics (or biomass).
Steps:
Plastic sourcing
Pre-treatment
CVD method (or pyrolysis/microwave)
Purified CNTs () - treating it with acid
Key Parameters within System Boundary
Energy Input: required for each process step.
Emission Output: released during each process step. *Energy Input:
Electricity powers processes, especially CVD.
Equipment has a power rating.
Indirect emissions result from electricity production methods.
Regional variations in emissions per kilowatt-hour.
per kilowatt hour in Uttarakhand (example).
Regional disparities in energy inputs and emissions exist.
Only three things are really important for system boundary
Energy, Substance Route, Emissions
Functional Unit
Reference material for comparison.
Example: 1 gram of CNT.
Used as a basis for comparing CNT synthesis impacts.
Yield adjustments may be needed to ensure functional unit represents an approximate value.
Not a control variable kind of thing
Different methods of CNT synthesis will vary in yield
Example:
5 grams of PET + 5 grams of paracetamol → 1.2 grams of CNTs.
Adjust input parameters so that the functional unit is 1 gram.
Functional unit: reference point for comparing environmental impact and energy production.
Assumed in a particular study for LCA purposes.
Ensures a level playing field when comparing different materials or processes.
Allows for the comparison of materials with the same quantities.
Further Steps (To be Discussed Next Time)
Calculations: require a dedicated session (30-40 minutes).
Previous Process of Plastic: Determine the amount of energy required for production (e.g., 10 grams of plastic).
Evaluate energy consumption (kilojoules, megajoules).
Determine environmental impact (GWP, AP, etc.).
*For producing 10 grams of plastic:
*How much energy is required?
*What is the environmental impact?
Tentative Data
Find existing literature on energy requirements and environmental impact for plastic production.
Compare different plastics.
LCA is always comparative early.Assume transportation distance to the facility (e.g., 15-20 kilometers).
CVD emissions are mostly indirect (electricity consumption).
Research Task
Determine the energy consumption and environmental impact for producing 10 grams of various plastics (polyethylene, polyester, mixed plastics).
Focus on one country (U.S. or India).
*First, India. If there are no results, consider the US.If the data is available from the US, take the electricity consumption and environmental impact of the USA and say it must be uniform somewhere.
Study Focus
*Find how much amount of energy is required to produce 10g of particular plastic
*What are the emissions?