LCIA Method Selection: ReCiPe, CML, TRACI, or EF?
Navigate the confusing landscape of LCIA methods—understand the differences, know when to use each, and interpret midpoint vs endpoint results correctly.
Prerequisites:
LCIA Method Selection: ReCiPe, CML, TRACI, or EF?
"Which LCIA method should I use?" is a question that confuses even experienced practitioners. This guide explains the differences between major methods and provides practical selection criteria.
Understanding LCIA Methods
What is an LCIA method? An LCIA method is a package containing:
- Impact category definitions
- Characterization factors for elementary flows
- (Optional) Normalization references
- (Optional) Weighting factors
Why so many methods? Different methods reflect:
- Different scientific models
- Different geographic contexts
- Different policy priorities
- Evolution of scientific understanding
Major LCIA Methods Compared
| Method | Origin | Categories | Approach | Best For |
|---|---|---|---|---|
| ReCiPe 2016 | Netherlands/Global | 18 midpoint, 3 endpoint | Comprehensive | General LCA |
| CML-IA | Netherlands | 11 midpoint | Academic standard | Research, baseline |
| TRACI 2.1 | US EPA | 10 midpoint | US-specific | US studies |
| EF 3.0 | EU | 16 midpoint | Regulatory | EU compliance |
| Impact 2002+ | Switzerland | 14 midpoint, 4 endpoint | Combined | Damage-focused |
| ILCD 2011 | EU JRC | 16 midpoint | Reference | EU baseline |
FAQ: LCIA Method Selection
"Which LCIA method should I use: ReCiPe, CML, TRACI, or EF?"
Quick decision framework:
| Your Context | Recommended Method |
|---|---|
| EU compliance/PEF | EF 3.0 (mandatory) |
| US-focused study | TRACI 2.1 |
| Academic research | ReCiPe or CML-IA |
| General consulting | ReCiPe 2016 |
| EPD creation | Check your PCR |
| Uncertainty matters | CML-IA (conservative) |
| Communication to non-experts | ReCiPe endpoints |
Method profiles:
ReCiPe 2016 - The versatile choice
- Pros: Comprehensive, both midpoint and endpoint, globally applicable
- Cons: More complex, three perspective variants
- Use when: You need flexibility and thorough analysis
CML-IA - The academic standard
- Pros: Well-established, widely cited, conservative approach
- Cons: Older (though updated), fewer categories than modern methods
- Use when: Academic publication, when tradition matters
TRACI 2.1 - The US choice
- Pros: US-specific characterization, EPA-developed
- Cons: Only applicable to US context
- Use when: US-based products, US regulatory context
EF 3.0 - The EU regulatory method
- Pros: Official EU method, harmonized with policy
- Cons: Mandatory for PEF, may not suit non-EU studies
- Use when: EU Product Environmental Footprint, EU compliance
When in doubt: Use ReCiPe 2016 (Hierarchist perspective) as your primary method, then test results with at least one other method for robustness.
"Why do midpoint and endpoint results differ so much?"
Understanding the difference:
Midpoint = Impact at the mechanism level
- "How much acidification potential?"
- Lower uncertainty, less intuitive
- Example: 15 kg SO₂-eq
Endpoint = Damage at the protection level
- "How much harm to ecosystems?"
- Higher uncertainty, more intuitive
- Example: 0.0003 species × year lost
Why results "differ":
They measure different things along the same cause-effect chain:
Emission → [Midpoint] → Damage mechanism → [Endpoint] → Actual harm
│ │ │
│ "Acidification "Ecosystem
│ Potential" damage"
│ │
└────────── Lower uncertainty ───────────────┘
│
Higher interpretation needed
Example: Climate change
| Level | Metric | Value | Interpretation |
|---|---|---|---|
| Midpoint | kg CO₂-eq | 100 | Radiative forcing potential |
| Endpoint | DALY | 0.0005 | Human health damage |
| Endpoint | species×yr | 0.002 | Ecosystem damage |
The endpoint modeling chain adds uncertainty:
- Climate models (temperature change per kg CO₂)
- Impact models (health effects per degree)
- Valuation models (DALYs per health effect)
Each step adds assumptions and uncertainty.
When to use each:
| Situation | Use Midpoint | Use Endpoint |
|---|---|---|
| Technical audience | ✓ | |
| Policy/management audience | ✓ | |
| Comparative claims | ✓ (lower uncertainty) | |
| Trade-off analysis | ✓ (easier to compare) | |
| Academic publication | ✓ (usually) | (supplementary) |
"How do I interpret normalization and weighting results?"
Normalization puts results in context:
Normalized value = Impact score / Reference value
Reference values are typically annual per-capita or regional totals.
Example:
- Your product's GWP: 10 kg CO₂-eq
- EU per-capita annual GWP: 8,000 kg CO₂-eq
- Normalized: 10/8,000 = 0.00125 person-equivalents
What normalization tells you:
- Which categories are relatively significant
- How your product compares to "average" activities
- NOT which impacts are more important
Weighting applies value judgments:
Weighted value = Normalized value × Weight factor
Weights reflect importance rankings, typically derived from:
- Expert panels
- Policy priorities
- Damage costs
- Distance-to-target
Critical notes on weighting:
ISO 14044 prohibits weighting for public comparative assertions. Weighted single scores should never be used to claim "Product A is better than Product B" in public communications.
Appropriate weighting use:
- Internal decision-making
- Screening and prioritization
- Sensitivity analysis ("how would ranking change?")
- Communication with clear caveats
"What impact categories are most relevant for my product type?"
Category relevance by product sector:
| Sector | Most Relevant Categories |
|---|---|
| Energy/fuels | Climate change, acidification, particulates |
| Agriculture | Eutrophication, land use, water use, climate |
| Mining/metals | Resource depletion, ecotoxicity, particulates |
| Chemicals | Human toxicity, ecotoxicity, climate |
| Electronics | Resource depletion (rare elements), climate, toxicity |
| Textiles | Water use, eutrophication, climate, toxicity |
| Construction | Climate, resource depletion, land use |
| Packaging | Climate, resource depletion, marine litter (emerging) |
| Transport | Climate, acidification, particulates, photochemical ozone |
Standard category sets:
Minimum set (most studies):
- Climate change (GWP)
- Ozone depletion
- Acidification
- Eutrophication (freshwater + marine)
- Photochemical ozone formation
- Resource depletion (fossil)
Extended set (comprehensive): Add:
- Human toxicity (cancer + non-cancer)
- Ecotoxicity (freshwater)
- Particulate matter
- Water use/scarcity
- Land use
- Ionizing radiation
Sector-specific additions:
- Mining: Resource depletion (minerals)
- Agriculture: Biodiversity, soil quality
- Marine products: Marine eutrophication
- Electronics: Rare earth depletion
Method Deep Dives
ReCiPe 2016
Structure:
- 18 midpoint categories
- 3 endpoint damage categories (Human Health, Ecosystems, Resources)
- 3 cultural perspectives (Individualist, Hierarchist, Egalitarian)
Perspectives explained:
| Perspective | Time Horizon | Optimism | Use When |
|---|---|---|---|
| Individualist | Short (20 yr) | Optimistic about tech fixes | Baseline for uncertainty range |
| Hierarchist | Medium (100 yr) | Moderate | Default recommendation |
| Egalitarian | Long (infinite) | Precautionary | Risk-averse analysis |
Default choice: ReCiPe 2016 Midpoint (H) - Hierarchist
CML-IA
Structure:
- 11 midpoint categories (baseline set)
- Additional categories in extended set
- No endpoint aggregation
Key characteristics:
- Conservative scientific approach
- Widely cited in literature
- Good for comparability with older studies
Categories:
- Abiotic depletion (elements + fossil)
- Global warming
- Ozone depletion
- Human toxicity
- Freshwater aquatic ecotoxicity
- Marine aquatic ecotoxicity
- Terrestrial ecotoxicity
- Photochemical oxidation
- Acidification
- Eutrophication
TRACI 2.1
Structure:
- 10 impact categories
- US-specific characterization factors
- Midpoint only
US-specific aspects:
- Ozone depletion uses US background
- Smog based on US conditions
- Toxicity using US population data
- Eutrophication for US water bodies
Categories:
- Ozone depletion
- Global warming
- Smog
- Acidification
- Eutrophication
- Human health (cancer + non-cancer)
- Respiratory effects
- Ecotoxicity
- Fossil fuel depletion
EF 3.0 (Environmental Footprint)
Structure:
- 16 impact categories (mandatory set)
- Normalization references (EU + global)
- Weighting factors (for single score, internal use only)
Regulatory context:
- Required for EU PEF studies
- Specified in EU Green Claims Directive proposals
- Linked to EU policy objectives
Key features:
- Climate change split: fossil, biogenic, land use change
- Water scarcity uses AWARE method
- Consistent with EU policy definitions
Practical Method Selection
Decision Flowchart
Start
│
▼
Is this for EU PEF compliance?
│ │
Yes No
│ │
▼ ▼
Use EF 3.0 Is this US-focused?
│ │
Yes No
│ │
▼ ▼
Use TRACI Academic publication?
│ │
Yes No
│ │
▼ ▼
Use CML-IA Use ReCiPe 2016
or ReCiPe (H) as default
Running Multiple Methods
Best practice: Run at least two methods and compare.
Comparison checklist: ☐ Are rankings consistent between methods? ☐ Do hotspots appear in same life cycle stages? ☐ Are conclusions robust to method choice?
If results differ significantly:
- Report the range
- Discuss which method is more appropriate
- Consider category-specific method selection
Software Implementation
openLCA: All major methods available via Nexus
SimaPro: Most methods built-in, some via updates
GaBi: Proprietary method variants + standards
Version matching: Ensure your LCIA method version matches your database version. Using ReCiPe 2016 with ecoinvent 3.5 is fine; mixing older methods with newer databases may cause characterization gaps.
Key Takeaways
- No single "best" method—choose based on context
- EF 3.0 is mandatory for EU PEF studies
- TRACI is required for US-specific characterization
- ReCiPe is versatile and widely applicable
- Midpoint has lower uncertainty; endpoint is more intuitive
- Weighting is prohibited for public comparative claims
- Test multiple methods to check robustness
Method Selection Checklist
Before finalizing your LCIA method:
☐ Check if regulation/standard mandates a specific method ☐ Consider geographic scope of your study ☐ Confirm method is available in your software ☐ Verify compatibility with your database version ☐ Decide if midpoint, endpoint, or both are needed ☐ Plan to test at least one alternative method ☐ Document rationale for method selection
Next Steps
With LCIA methods understood, the next lesson is our Process Modeling Cookbook—practical recipes for modeling common processes like electricity, transportation, and manufacturing.