How to Conduct Life Cycle Assessments (LCA) for Industrial Products

Life cycle assessment process for an industrial product from raw materials and manufacturing to use and end-of-life
Industrial Sustainability Methodology

A life cycle assessment helps an industrial team look beyond the factory gate. It connects raw materials, manufacturing, logistics, product use, maintenance, and end-of-life treatment so decisions are based on the complete product system rather than one visible environmental claim.

Industrial products often carry environmental impacts that are not obvious from production records alone. A lightweight component may require an energy-intensive alloy. An efficient manufacturing process may produce a product that consumes large amounts of electricity during operation. A recyclable material may still be discarded if no practical collection system exists in the target market.

Life cycle assessment, commonly shortened to LCA, provides a structured method for identifying these trade-offs. It can support product design, material selection, supplier evaluation, energy-efficiency projects, packaging changes, customer reporting, procurement requirements, and environmental improvement plans.

An LCA should not be treated as a machine that produces one perfect sustainability score. Its conclusions depend on the goal, functional unit, system boundary, data quality, allocation rules, impact method, assumptions, and interpretation. A useful study makes these choices visible instead of hiding them behind a chart.

Practical principle: begin with the decision the study must support. Do not start by opening software and collecting every available number. A clear goal prevents wasted work and determines which data, boundaries, scenarios, and review level are actually needed.

What the Product Life Cycle Includes

A product life cycle links the processes required to deliver a defined function. Depending on the study, this may include extraction of resources, production of materials, component manufacturing, factory operations, packaging, transport, installation, use, repair, replacement parts, recycling, energy recovery, and disposal.

Raw Materials
Suppliers
Manufacturing
Distribution
Use and Service
End of Life

Not every study needs the same boundary. An internal screening assessment may focus on the stages most relevant to an early design decision, while a public product comparison normally requires stronger data, greater transparency, consistent comparison rules, and appropriate review.

The Four Connected Phases of an LCA

The recognized LCA framework is organized around four connected phases. These phases are iterative, meaning that new information may require the team to return to an earlier decision and improve the model.

Direction

Goal and Scope

Define why the study is being performed, who will use it, what function is assessed, which processes are included, and what level of evidence is required.

Data

Life Cycle Inventory

Quantify materials, energy, fuels, water, transport, emissions, waste, components, maintenance, and other flows connected to the product system.

Evaluation

Impact Assessment

Translate inventory flows into selected environmental impact indicators using an appropriate assessment method.

Decision

Interpretation

Identify hotspots, test assumptions, evaluate limitations, check consistency, and develop conclusions that match the original goal.

The phases should not be treated as a one-way checklist. If inventory collection reveals that an excluded supplier process is important, the scope may need to change. If sensitivity testing reverses the conclusion, the team may need better data before making a decision.

Define the Goal Before Collecting Data

The goal statement explains why the LCA exists and how its results will be used. A vague goal such as “measure how sustainable the product is” provides little guidance. A useful goal is connected to a specific decision.

Possible Goal Decision Supported Likely Study Requirement
Internal hotspot screening Identify which materials or processes deserve improvement first Screening data
Material comparison Compare alternative alloys, polymers, packaging, or components Equal function
Supplier evaluation Compare production routes or sourcing regions Supplier evidence
Customer or tender reporting Provide documented environmental information to a buyer Transparent report
Public comparative claim Communicate that one product performs better than another High review level
Environmental Product Declaration Publish standardized product information under an applicable program Category rules

Questions the Goal Statement Should Answer

  • What decision will the results support?
  • Who is the intended audience?
  • Will the results remain internal or be published?
  • Are competing products being compared?
  • Which environmental issues are most relevant?
  • What accuracy and review level are necessary?
  • Which geographic market is represented?
  • What time period should the data reflect?

Create a Fair Functional Unit

The functional unit describes the measurable service delivered by the product. It is the reference against which all material, energy, transport, maintenance, and waste flows are calculated.

Comparing “one product” with “one product” is often misleading. Products can differ in capacity, efficiency, durability, repair frequency, load, operating hours, or expected lifetime. The comparison should reflect equivalent performance.

Hypothetical Industrial Pump Example

Comparing one pump against another may ignore efficiency and service life. A more useful functional unit could describe the movement of a defined volume of liquid at a specified pressure over a defined operating period.

Function Move a defined quantity of liquid through the industrial process.
Performance Specified flow rate, pressure, duty cycle, and operating conditions.
Time Expected operating hours or service life represented by the study.

A good functional unit is specific enough to support a fair comparison but understandable enough that engineers, purchasers, sustainability teams, and reviewers can apply it consistently.

Do not change the functional unit after seeing which option performs better. The comparison basis should be defined before results are calculated and should remain connected to the real service expected from the product.

Select the Appropriate System Boundary

Production focus

Cradle to Gate

Includes raw material extraction, upstream processing, purchased components, and manufacturing until the product leaves the factory.

It is commonly useful for intermediate products, supplier information, and manufacturing improvement.

Full product life

Cradle to Grave

Continues beyond manufacturing to include distribution, installation, use, maintenance, replacement, and end-of-life treatment.

It is particularly important for products that consume energy or require frequent service.

Circular scenario

Cradle to Cradle

Examines how materials or components can return to another productive cycle through reuse, remanufacturing, or recycling.

Recovery assumptions must reflect realistic collection and processing systems.

The boundary should include processes capable of influencing the conclusion. Exclusions should be documented and justified. A process should not be excluded only because its data are difficult to obtain.

Use-phase warning: for electric motors, pumps, compressors, refrigeration equipment, industrial controls, and other energy-consuming products, operating electricity may dominate the result. A production-only study could miss the most important improvement opportunity.

Step-by-Step LCA Workflow

  1. Write the goal statement.
    Define the decision, intended audience, planned use of results, required level of detail, and whether the study will support a public claim.
  2. Set the functional unit.
    Describe the measurable function, capacity, performance conditions, expected lifetime, and operating profile represented by the model.
  3. Draw the system boundary.
    Map included suppliers, manufacturing processes, logistics, use, maintenance, replacement, recycling, and disposal activities.
  4. Establish data-quality requirements.
    Set expectations for geography, technology, age, source, completeness, consistency, and uncertainty.
  5. Build the life cycle inventory.
    Collect quantities for materials, components, energy, fuels, water, transport, packaging, emissions, waste, maintenance, and end-of-life flows.
  6. Resolve shared-process allocation.
    Determine how common energy, equipment, co-products, scrap, recycling, and shared production lines will be represented.
  7. Select the impact-assessment method.
    Choose impact categories and characterization methods that match the study’s goal, location, product type, and reporting framework.
  8. Check and calculate the model.
    Verify units, mass balances, energy balances, transport distances, conversion factors, cut-offs, signs, and links between processes.
  9. Interpret results and test scenarios.
    Identify hotspots and test product life, energy mix, transport, recycling, allocation, scrap, maintenance, and other influential assumptions.
  10. Report conclusions with limitations.
    Explain the method, data, exclusions, uncertainty, review status, and conditions under which the conclusions remain valid.

Build a Reliable Life Cycle Inventory

The life cycle inventory is the quantitative foundation of the study. It records the resources entering the system and the products, emissions, waste, and other flows leaving it.

Primary data come directly from the manufacturer, supplier, site, or product being studied. Secondary data come from databases, government publications, research, industry datasets, and other representative sources. Primary data are often preferred for important manufacturing processes, but secondary data remain necessary for many upstream materials and background systems.

Inventory Area Possible Data Source Quality Check
Bill of materials Engineering records, ERP data, drawings, supplier specifications Confirm grades, weights, coatings, electronics, fasteners, and scrap
Factory electricity Utility bills, submetering, machine data, production records Use an allocation method that reflects actual production
Fuels and process heat Fuel invoices, boiler meters, furnace records Check units, heating values, efficiency, and shared use
Transport Logistics invoices, supplier locations, shipping records Verify distance, vehicle, load factor, route, and return trips
Use-phase energy Product testing, field data, operating profiles, customer records Represent realistic duty cycles rather than ideal conditions only
Maintenance Service manuals, warranty data, maintenance systems Include replacement parts, travel, consumables, and frequency
End of life Waste contractors, recyclers, industry data, local statistics Avoid assuming perfect collection or recycling

Evaluate Data Quality Across Four Dimensions

Time Does the dataset represent current production and technology?
Geography Does it match the country, grid, transport system, or market?
Technology Does it represent the actual material grade and production route?
Completeness Are important flows included, measured, estimated, and documented?

Detailed weak data are not automatically better than simpler reliable data. Focus collection effort on flows that may influence the result, and clearly record where estimates or representative datasets are used.

Choose Relevant Impact Categories

A complete LCA is broader than a product carbon footprint. Climate change may be a major category, but industrial products can also create important trade-offs involving resources, air pollution, water, chemicals, land, and nutrient emissions.

Climate Change Potential contribution from greenhouse gas emissions across the product system.
Resource Use Potential pressure associated with minerals, metals, fossil resources, and other inputs.
Acidification Potential effects associated with acidifying emissions to air and other environmental media.
Eutrophication Potential nutrient enrichment effects involving emissions to freshwater, marine, or terrestrial systems.
Water Use Potential impacts connected to water consumption and regional water conditions.
Particulate Matter Potential health-related effects associated with particulate-forming emissions.

Other categories may include ozone formation, land use, ecotoxicity, human toxicity-related indicators, ionizing radiation, and ozone depletion. The selected method should match the study’s purpose and should be applied consistently across the products or scenarios being compared.

Do not hide trade-offs inside one combined score. Weighting and normalization may be useful in some methods, but they include methodological and value choices. Show important category-level results so decision-makers can understand why one option performs differently.

Identify Hotspots Before Choosing Improvements

A hotspot is a material, process, life cycle stage, component, or assumption that contributes strongly to one or more impact categories. The purpose of hotspot analysis is to direct attention toward changes capable of producing meaningful improvement.

Hypothetical Hotspot Result

Imagine that an industrial machine assessment finds most climate impact in operating electricity, followed by steel production and replacement parts.

  • Improving operating efficiency may deserve first priority.
  • Reducing packaging may still help, but may not change the overall conclusion.
  • Material changes should not reduce efficiency or service life.
Product Use
Materials
Maintenance
Transport
Packaging

The chart above is illustrative and does not represent a specific product. Real contributions must come from the study’s inventory data, impact method, and defined functional unit.

Use Sensitivity and Scenario Analysis

Sensitivity analysis checks whether the conclusion remains stable when important assumptions change. It is one of the most useful protections against false confidence.

  • Test different product lifetimes
  • Compare regional electricity mixes
  • Change annual operating hours
  • Test low and high recycling rates
  • Compare transport routes and distances
  • Change manufacturing scrap assumptions
  • Test alternative allocation methods
  • Compare repair and replacement scenarios
  • Evaluate different material datasets
  • Test optimistic and conservative end-of-life cases

If a small change in one assumption reverses the preferred option, the result is sensitive. The report should explain this clearly, and the team should consider collecting stronger data before approving a major design or procurement decision.

A range can be more honest than one precise number. When data uncertainty is meaningful, reporting scenarios or intervals can communicate the result more responsibly than presenting a single value with false precision.

Common Errors That Can Distort Results

Common Error Why It Matters Better Practice
Comparing one item with one item Products may deliver different capacity, efficiency, or lifetime Compare an equal functional service
Ignoring use-phase electricity Operating energy may be the largest impact source Model realistic duty cycles and service life
Using a different boundary for each option One product may appear better because important stages were excluded Apply consistent boundaries and rules
Assuming perfect recycling The model may credit recovery that does not occur in practice Use market-specific collection and processing scenarios
Mixing kilograms, grams, megajoules, and kilowatt-hours Unit errors can change results by orders of magnitude Use controlled units and independent model checks
Using outdated or mismatched datasets The model may not represent the current technology or region Record dataset age, geography, and production route
Focusing only on carbon Important water, resource, toxicity, or pollution trade-offs may be hidden Select categories based on the product and study goal
Publishing comparative claims without suitable review Weak methods can create credibility, commercial, or legal risks Use recognized rules and qualified independent review

Turn Results Into Industrial Improvements

The final report is not the main value of an LCA. The value appears when the findings lead to measurable improvements in design, sourcing, production, logistics, operation, maintenance, or recovery.

Identified Hotspot Possible Improvement Path Trade-Off to Check
High use-phase electricity Improve efficiency, controls, maintenance, and operating guidance Cost, reliability, and performance under real loads
High-impact metal production Reduce mass, use qualified recycled content, or extend service life Strength, corrosion, fatigue, and supplier consistency
Frequent component replacement Improve durability, repairability, and preventive maintenance Added material, complexity, and maintenance access
Long-distance transport Regional sourcing, improved loading, packaging redesign, or modal shift Supplier quality, lead time, and inventory risk
Low end-of-life recovery Simplify material separation, label components, create take-back systems Actual collection participation and recycler acceptance

Before changing a product specification, test whether the proposed improvement shifts impacts to another stage. Reducing material mass is not helpful if it shortens the product’s life. Adding recycled content may be beneficial, but not if inconsistent quality produces more scrap or field failures.

Reporting and Review

An LCA report should allow a knowledgeable reader to understand how the conclusions were produced. The level of detail should match the intended audience and use of the study.

A Clear Report Should Include

  • Goal and intended application
  • Intended audience and publication status
  • Functional unit and reference flow
  • System boundary and process map
  • Cut-off and allocation rules
  • Primary and secondary data sources
  • Data-quality and uncertainty discussion
  • Impact-assessment method and categories
  • Hotspots and scenario results
  • Sensitivity and consistency checks
  • Limitations and excluded processes
  • Conclusions that match the defined goal

Independent review becomes especially important when results will be published, used in procurement requirements, presented to customers as formal evidence, or used to compare competing products. Product category rules or program-specific requirements may also apply to Environmental Product Declarations and other standardized communications.

Do not turn a conditional result into an unlimited marketing claim. A conclusion that applies to one region, electricity mix, product life, boundary, or operating profile should not be presented as universally true.

Practical Recommendation

Companies new to LCA can begin with an internal screening study focused on one clearly defined product and decision. Start with a process map, bill of materials, factory energy, major suppliers, transport, realistic use conditions, maintenance, and end-of-life assumptions.

Use the screening results to identify the processes that deserve better data. There is little value in spending weeks refining a minor packaging flow if product electricity consumption or a major metal component dominates the result.

As the study moves toward public communication, product comparisons, formal declarations, procurement rules, or regulatory use, increase the level of documentation, methodological consistency, data verification, and professional review.

A credible industrial LCA does not promise certainty that the data cannot support. It gives decision-makers a transparent view of the product system, the most important environmental hotspots, the assumptions that influence the result, and the improvement options most likely to create meaningful change.

Frequently Asked Questions

Is a carbon footprint the same as a life cycle assessment?

No. A product carbon footprint focuses on climate-change impacts associated with greenhouse gas emissions. An LCA may include climate change together with other categories such as resource use, water use, acidification, eutrophication, particulate matter, and toxicity-related indicators.

Can a company perform an LCA using a spreadsheet?

A spreadsheet can support an early screening study when the product system is relatively simple and the goal is internal learning. Detailed studies normally benefit from specialized LCA software, recognized inventory databases, controlled calculations, and experienced practitioners.

What should a company do when supplier data are unavailable?

Request primary data for important components first. When that is not possible, use a reputable secondary dataset that matches the material, technology, region, and time period as closely as possible. Document the substitution and test whether it changes the conclusion.

How often should an industrial LCA be updated?

Review the study when major suppliers, materials, manufacturing processes, product design, energy sources, transport routes, use conditions, or end-of-life assumptions change. Background datasets may also become outdated even when the product remains unchanged.

What is allocation in an LCA?

Allocation is the method used to divide shared inputs and outputs between products or functions. It may be needed when several products share a production line, one process produces multiple outputs, or recycling creates benefits and burdens across different product systems. The chosen rule should be justified and tested when it can influence the result.

Can two LCA results be compared directly?

Only when important methodological conditions are compatible. The studies should represent equivalent functions and use consistent boundaries, data-quality expectations, allocation approaches, impact methods, geographic assumptions, and reporting rules. Two published numbers are not automatically comparable.

When should an external specialist be involved?

External support is especially useful for complex supply chains, public claims, product comparisons, Environmental Product Declarations, customer tenders, regulatory reporting, sensitive allocation questions, and studies where internal teams lack suitable LCA experience.

Official References and Further Reading

Editorial note: This article was prepared by the Ogumex Editorial Team for educational purposes. Formal LCAs, public comparative claims, Environmental Product Declarations, procurement disclosures, and regulatory submissions should follow the applicable standards, category rules, program requirements, and professional review procedures.