Allocation Methods: A Practical Decision Guide
Navigate the complexities of allocation in LCA—when to use mass vs. economic allocation, how to handle multi-output processes, and managing recycled materials.
Prerequisites:
Allocation Methods: A Practical Decision Guide
"When should I use economic vs. mass allocation?" is one of the most debated questions in LCA. This guide provides practical decision frameworks for handling multi-output processes, recycling, and other allocation challenges.
What Is Allocation?
The problem: Many industrial processes produce multiple products from a single input.
Example: Oil refinery
- Input: 1,000 kg crude oil
- Outputs: 400 kg gasoline, 300 kg diesel, 200 kg kerosene, 100 kg asphalt
Which product "owns" the refinery's environmental impacts?
Allocation divides the impacts among co-products using some rationale.
The ISO 14044 Allocation Hierarchy
ISO standards recommend this order of preference:
- Avoid allocation by subdividing processes
- Avoid allocation by system expansion
- If allocation is unavoidable, use physical relationships
- If physical relationships don't work, use other relationships (e.g., economic value)
In practice, most practitioners jump to allocation because subdivision and system expansion are often impractical. That's okay—just document your reasoning.
FAQ: Allocation Decisions
"When should I use economic vs. mass allocation?"
Quick decision guide:
| Use Mass Allocation When: | Use Economic Allocation When: |
|---|---|
| Products have similar function | Products have different functions |
| Physical causality is clear | Market value reflects "purpose" |
| PCR/standard requires it | PCR/standard requires it |
| Prices are volatile | Mass ratio doesn't reflect value |
| You want reproducibility | You want to reflect market drivers |
The deeper answer:
Mass allocation distributes impacts by weight:
Share_product = mass_product / total_mass_outputs
Pros:
- Simple, reproducible
- Stable over time
- Easy to verify
Cons:
- Ignores that a small byproduct may drive the process
- May not reflect economic reality
Economic allocation distributes impacts by revenue:
Share_product = (mass × price)_product / total_revenue
Pros:
- Reflects market causality
- Valuable products "own" more impacts
- Aligns with business decisions
Cons:
- Prices fluctuate (results become time-dependent)
- Price data can be confidential
- Different markets have different prices
Worked example: Soybean processing
Soybean crushing produces:
- 800 kg soybean meal (animal feed)
- 180 kg soybean oil (food)
- 20 kg hulls (waste/low value)
| Allocation Method | Meal Share | Oil Share |
|---|---|---|
| Mass allocation | 82% | 18% |
| Economic allocation (example prices) | 45% | 54% |
Oil is more valuable per kg, so economic allocation shifts impacts toward it.
When in doubt: Check if a PCR or standard applies—it usually specifies the allocation method. If not, run both and report the range.
"How do I handle multi-output processes?"
Step-by-step approach:
Step 1: Can you subdivide? Split the process into sub-processes that each produce one output.
Example: A factory makes two products on separate production lines. Measure each line's energy use separately.
If subdivision isn't possible (shared equipment, joint production), move to Step 2.
Step 2: Can you use system expansion? Expand your system to include the avoided production of the co-product.
Example: Cement kiln uses waste fuels. Credit the system for avoided waste treatment.
Net impact = Process impact - Avoided treatment impact
If system expansion creates modeling complexity or lacks suitable proxies, move to Step 3.
Step 3: Choose an allocation basis
| Basis | When Appropriate | Example |
|---|---|---|
| Mass | Similar products, bulk commodities | Meat cuts from cattle |
| Energy | Energy carriers | Refinery products by energy content |
| Economic | Different-function co-products | Grain + straw |
| Physical causality | Clear causal link | Emissions by stoichiometry |
Step 4: Apply consistently Use the same allocation approach throughout your study for comparable processes.
Step 5: Test sensitivity Report how results change under alternative allocation methods.
"What's the difference between allocation and system expansion?"
Allocation: Divides impacts among co-products
Process A → Product 1 (gets 60%)
→ Product 2 (gets 40%)
System expansion: Credits avoided production of displaced product
Process A → Product 1 (gets all impacts)
→ Product 2 (credits avoided alternative production)
Practical comparison:
Scenario: A bioethanol plant produces ethanol and animal feed (DDGS).
Allocation approach:
- Total process: 1,000 kg CO₂
- Ethanol (60% economic value): 600 kg CO₂
- DDGS (40% economic value): 400 kg CO₂
System expansion approach:
- Total process: 1,000 kg CO₂
- Ethanol takes all: 1,000 kg CO₂
- DDGS displaces soybean meal: -200 kg CO₂ credit
- Net for ethanol: 800 kg CO₂
Which is "right"?
- Allocation is simpler and more reproducible
- System expansion is theoretically preferred by ISO but requires identifying what's displaced
- Consequential LCA typically uses system expansion
- Attributional LCA typically uses allocation
"How do I allocate impacts for recycled materials?"
This is one of LCA's most contested topics. See our Advanced: System Boundary Approaches lesson for complete coverage.
Quick summary of approaches:
Cut-off (recycled content) approach:
- Recycled input arrives "burden-free"
- End-of-life recycling burden goes to next life cycle
- ecoinvent "Cut-off" system model uses this
End-of-life (substitution) approach:
- Recycled input carries virgin-equivalent burden
- End-of-life recycling earns credit for avoided virgin production
- ecoinvent "APOS" uses a variant
Circular Footprint Formula (CFF):
- Shares burdens between life cycles (50/50 default)
- EU PEF method uses this
- Accounts for quality changes
Decision guide for recycling allocation:
| Context | Recommended Approach |
|---|---|
| Most EPDs | Cut-off (check PCR) |
| EU PEF studies | Circular Footprint Formula |
| Design for recyclability | End-of-life allocation |
| Simple screening | Cut-off |
Don't mix approaches! Using cut-off for material input AND claiming end-of-life recycling credits is double-counting. Be consistent.
Allocation in Common Situations
Agriculture: Crop + Residue
Example: Wheat grain + wheat straw
| Method | Grain Share | Straw Share |
|---|---|---|
| Mass (1:1 ratio) | 50% | 50% |
| Economic (grain 10× straw price) | 91% | 9% |
| Energy content | 60% | 40% |
Common practice: Economic allocation (straw is a byproduct, not the reason for farming).
Meat Processing: Multiple Cuts
Example: Cattle produces beef cuts, organs, hide, bones
Approaches:
- Mass: All meat is equal per kg
- Economic: Premium cuts get more; bones/organs get less
- Biophysical: Based on protein content or nutritional value
Common practice: Economic allocation (market value reflects desirability).
Petroleum Refining
Products: Gasoline, diesel, jet fuel, LPG, asphalt, petrochemicals
Approaches:
- Mass: Simple but ignores that refinery adjusts for market demand
- Economic: Reflects market drivers but prices are volatile
- Energy: Logical for fuels but ignores non-fuel products
Common practice: Energy content (for fuels) or economic (for mixed products).
Recycling: Open-Loop
Example: PET bottle → recycled fiber (different product)
Challenge: Quality changes. Recycled fiber isn't equivalent to virgin PET.
Solution: Quality factors in CFF, or substitution ratio <1 in end-of-life approach.
Combined Heat and Power (CHP)
Products: Electricity + heat
| Method | Electricity Share | Heat Share |
|---|---|---|
| Energy content (exergy) | ~65% | ~35% |
| Economic | Varies by market | Varies by market |
| System expansion | Full impact - avoided heat | Credit only |
Common practice: Exergy-based allocation or system expansion (crediting avoided heat from boiler).
When Allocation Goes Wrong
Common Mistakes
Mistake 1: Ignoring byproducts Assigning all impacts to the main product when byproducts are significant.
Mistake 2: Using mass when economic makes sense Animal feed byproducts shouldn't share impacts equally with food products.
Mistake 3: Inconsistent allocation within a study Using mass allocation for one process, economic for another, without justification.
Mistake 4: Double-counting recycling Claiming both "recycled content" benefits AND "end-of-life recycling" credits.
Mistake 5: Not testing sensitivity Allocation choices can change results dramatically—always test alternatives.
When Allocation Really Matters
Allocation is most critical when:
- Co-product value is similar to main product
- Your product is actually a byproduct of another industry
- Recycled content is a significant fraction
- Results will be used for comparative claims
Practical Recommendations
Default Choices by Sector
| Sector | Common Allocation Approach |
|---|---|
| Agriculture | Economic |
| Petroleum | Energy or economic |
| Metal processing | Mass or economic |
| Waste treatment | System expansion |
| Recycling | Cut-off (most EPDs) |
| Food processing | Economic |
Sensitivity Analysis Protocol
Always test:
- Your chosen allocation method
- At least one alternative method
- Report the range of results
If results change significantly (>20%), discuss implications in your conclusions.
Documentation Checklist
For each allocated process, document:
- Products and their masses/values
- Allocation basis chosen
- Rationale for choice
- Sensitivity to alternatives
- Data sources for allocation factors
Key Takeaways
- Try to avoid allocation first (subdivision, system expansion)
- Mass allocation is simple but may not reflect causality
- Economic allocation reflects market drivers but is less stable
- Recycling allocation is complex—use approaches consistently
- Sensitivity analysis is essential—test alternatives
- Check your PCR/standard—it often specifies the method
Decision Flowchart
Multi-output process
│
▼
Can you subdivide?
│ │
Yes No
│ │
▼ ▼
Subdivide Can you use system expansion?
│ │ │
│ Yes No
│ │ │
│ ▼ ▼
│ Expand Products similar?
│ │ │
│ Yes No
│ │ │
│ ▼ ▼
│ Mass Economic
│ │ │
└────────────────────────┴─────────┘
│
▼
Document & test sensitivity
Next Steps
With allocation understood, the next lesson covers Data Collection & Gap-Filling Strategies—practical techniques for dealing with missing data.