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Comparative LCA Case Study: EV Battery vs ICE System | DEISO

Comparative LCA of an EV Battery Pack and an ICE Powertrain System

This illustrative case study demonstrates how DEISO can structure a comparative life cycle assessment between two alternative vehicle propulsion-related product systems: an electric vehicle battery pack and an internal combustion engine powertrain system. The purpose is to show how side-by-side LCA can support technology comparison, design decisions, and strategic environmental evaluation.

Case Positioning

This is an illustrative technical case study prepared to demonstrate DEISO’s comparative LCA approach. It does not represent a real client engagement, a real vehicle manufacturer, or confidential product data. It is intended as a representative scenario showing how comparative lifecycle thinking can reveal environmental trade-offs between two alternative technology pathways.

Scenario Overview
  • Comparison type: Product-versus-product comparative LCA
  • Option A: EV battery pack for passenger vehicle application
  • Option B: ICE powertrain component system for passenger vehicle application
  • Goal: Evaluate relative environmental burdens and trade-offs
  • Assessment focus: Impact comparison across categories, normalized interpretation, and sensitivity analysis
  • Decision relevance: Product strategy, procurement, design evaluation, and technology transition insight
Business Context

Organizations comparing electrified and conventional technologies often need more than a headline carbon number. They need a structured understanding of where the burdens occur, which impact categories shift, and how sensitive the result is to assumptions such as electricity mix, recycling rates, and system boundaries. This is especially important in product design, procurement, and strategic communication.

In this illustrative case, the comparison focuses on the product-stage environmental profile while also introducing use-phase sensitivity logic. This allows decision-makers to see why simplified claims can be misleading when lifecycle stages are excluded or when assumptions remain implicit.

DEISO Technical Approach

DEISO’s methodological workflow for this type of comparative LCA includes:

  • Clarification of functional equivalence and comparison objective
  • Definition of system boundaries and lifecycle stages
  • Compilation of material, manufacturing, and logistics data for each option
  • Impact assessment across multiple environmental categories
  • Normalization and side-by-side interpretation of results
  • Sensitivity analysis for key assumptions such as grid mix, recycling, and use-phase conditions
Illustrative Results Summary
Product-Stage Comparison

At the manufacturing and product stage, the EV battery pack showed higher impacts across all illustrated environmental categories. The largest divergence was observed in mineral resource scarcity, followed by global warming potential and acidification potential. This reflects the material intensity and upstream processing requirements associated with lithium-ion battery production.

Category-Level Insight

The comparison demonstrates that the environmental difference between product options is not uniform across categories. Climate change, resource depletion, and acidification each behave differently depending on material composition, energy source, and system design. For this reason, comparative LCA should not rely on a single indicator alone.

Sensitivity Effects

Sensitivity analysis showed that low-carbon electricity sourcing and improved recycling can materially reduce the manufacturing-stage burden of the EV battery system. However, under the product-stage-only comparison, the ICE powertrain system remained lower in environmental burden. When extended use-phase assumptions and a decarbonized grid were considered, the EV pathway became more favorable at the broader system level.

Hotspot Interpretation
EV Battery Pack

The dominant hotspots for the EV battery system were raw material extraction and refining, especially for critical minerals and battery-grade materials. Manufacturing energy also contributed meaningfully, while transport and end-of-life were secondary in comparison.

ICE Powertrain System

For the ICE powertrain system, impacts were more strongly linked to metals production, casting, machining, and component manufacturing. The burden profile was less dominated by mineral scarcity than the EV option, but still environmentally significant.

Strategic Implications

This illustrative case shows why decision-makers need comparative LCA rather than simplified environmental claims. A product system that is more burdensome during manufacturing may still perform better under full lifecycle conditions if its use phase benefits are substantial. Conversely, a lower-burden manufacturing option may not remain favorable once operation-phase emissions are included.

The case also shows that comparative LCA is highly sensitive to boundary definition, data assumptions, and scenario design. Therefore, it is most valuable when treated as a structured decision-support method rather than a marketing simplification.

Decision Guidance
  • Use comparative LCA when evaluating alternative designs or technologies
  • Ensure functional equivalence is clearly defined before comparison
  • Interpret multiple impact categories rather than carbon alone
  • Test sensitivity to electricity mix, recycling, and system boundary assumptions
  • Use scenario analysis to avoid misleading conclusions from product-stage-only results
Conclusion

This illustrative comparative LCA demonstrates how side-by-side environmental analysis can reveal the real trade-offs between an EV battery system and an ICE propulsion-related alternative. By organizing results across multiple categories, normalizing differences, and testing sensitivity assumptions, DEISO helps decision-makers move beyond simplified narratives toward more robust environmental evaluation.

For organizations working on product strategy, technology transition, procurement, or technical communication, this type of comparative LCA can provide the analytical foundation needed for stronger and more defensible decisions.

Illustrative Case Disclaimer

This case study represents a technical demonstration scenario created to illustrate comparative LCA structure, side-by-side impact interpretation, normalized results, and sensitivity analysis logic. It does not represent a real client project, real product dataset, or confidential company information.

Illustrative Comparative LCA Dashboard — EV Battery Pack vs ICE Powertrain System

Passenger Vehicle Application | Product-to-Product Comparative Assessment | Environmental Trade-off Analysis | Illustrative Technical Demonstration

Functional Basis
1 propulsion system
Passenger vehicle application
Higher Manufacturing GWP
EV Battery Pack
Material-intensive production stage
Use-Phase Advantage
EV Pathway
Under low-carbon electricity scenario
Decision Insight
Trade-off Driven
Manufacturing burden vs use-phase benefit
Option A — EV Battery Pack
Chemistry: NMC-type lithium-ion battery
Application: passenger EV platform
Assessed stages: raw materials, production, transport, use sensitivity, end-of-life scenario
Main burden driver: lithium, nickel, cobalt, graphite, energy-intensive manufacturing
Option B — ICE Powertrain System
System: engine block, transmission-related propulsion component set
Application: conventional passenger vehicle platform
Assessed stages: metals production, manufacturing, transport, fuel-use sensitivity, end-of-life scenario
Main burden driver: steel, aluminum casting, machining, operational fuel dependence
Impact Category Comparison
Impact Category Unit EV Battery Pack ICE Powertrain Relative Difference Interpretation
Global warming potential kg CO2e 5,860 2,940 +99% EV battery manufacturing burden significantly higher at product stage
Acidification potential kg SO2 eq 28.4 16.7 +70% Mining and refining increase upstream burden for EV battery materials
Eutrophication potential kg PO4 eq 4.1 2.6 +58% Higher upstream material extraction drives nutrient-related impacts
Photochemical ozone formation kg NMVOC eq 12.3 10.5 +17% Difference is narrower than GWP due to broader industrial contributions
Abiotic depletion potential – fossil MJ 42,800 31,500 +36% Battery production remains energy-intensive even before vehicle operation
Mineral resource scarcity kg Cu eq 8.9 3.2 +178% Critical minerals strongly influence EV-side resource pressure
Normalized Comparison Index
GWP
EV 100
ICE 50
Acidification
EV 100
ICE 59
Eutrophication
EV 100
ICE 63
POCP
EV 100
ICE 85
ADP Fossil
EV 100
ICE 74
Mineral Scarcity
EV 100
ICE 36
Normalized results use the EV battery pack as the 100 reference baseline to show relative burden intensity across categories.
Headline Interpretation
🔴 EV battery pack shows higher manufacturing-stage burdens across all illustrated categories.
🔴 Mineral scarcity is the most divergent category.
🟠 Climate burden difference is substantial at product stage.
🟢 EV option becomes favorable only when use-phase electricity is sufficiently decarbonized.
🟢 Decision quality depends strongly on system boundary and use-phase assumptions.
Lifecycle Contribution Comparison
EV Battery Pack
Raw Material Extraction 67%
Manufacturing Energy 8%
Transport 15%
End-of-Life / Recovery 10%
ICE Powertrain
Metals Production 49%
Manufacturing / Machining 21%
Transport 18%
End-of-Life / Recovery 12%
Sensitivity Analysis
Scenario EV System GWP ICE System GWP Relative Position Decision Meaning
Baseline manufacturing comparison 5,860 2,940 ICE lower Product-stage only view favors ICE-side component system
Low-carbon electricity for battery production 4,920 2,940 ICE lower Battery burden improves materially but remains higher at production stage
High recycled metals recovery 4,580 2,710 ICE lower Recovery helps both, but EV still remains higher in this stage-specific view
Extended use-phase, decarbonized grid scenario System-favorable System-burdened EV lower Once use-phase is included under favorable grid conditions, EV pathway can outperform
What This Comparison Shows
🔴 EV battery systems are not automatically lower-impact at manufacturing stage.
🔴 Product-stage comparisons can mislead if use phase is excluded.
🔴 Mineral intensity changes the burden profile significantly.
🔴 Category-by-category interpretation matters more than single-number simplification.
Decision Guidance
✅ Use comparative LCA for procurement and design trade-off decisions.
✅ Keep functional equivalence and system boundary explicit.
✅ Add use-phase scenarios before making strategic claims.
✅ Test recycling, grid mix, and service-life assumptions before concluding.
Need a Comparative LCA for Product Design, Procurement, or Technology Decisions?

DEISO supports organizations with comparative life cycle assessments, trade-off interpretation, scenario testing, and technical review to help decision-makers evaluate alternatives with stronger methodological confidence.

Contact DEISO
Illustrative Case Disclaimer: This dashboard and case study represent a technical demonstration scenario created to illustrate comparative LCA structure, side-by-side impact interpretation, normalized results, and sensitivity analysis logic. It does not represent a real client project, real product dataset, or confidential company information.
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