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Life Cycle Assessment, Explained

LCA fixes the method, not the answer. What the four phases actually involve, where the judgement calls sit, and how to read someone else’s study critically.

CirculeID Research6 min read1,270 words

Life cycle assessment quantifies environmental impacts across a product’s life through four phases: goal and scope definition, inventory analysis, impact assessment and interpretation. ISO 14040 and 14044 standardise the method rather than the result, which is why two compliant studies can differ substantially.

What this gives you

What a life cycle assessment does and does not tell you, how boundary choices change the number, and which parts of an LCA belong in the passport.

Key takeaways

  • The goal and scope phase determines the answer more than the data collection does.
  • Inventory analysis is where most of the effort goes and where primary data matters most.
  • Impact assessment converts flows into categories, and the choice of method affects the result.
  • A study without its functional unit, boundary and allocation rules cannot be compared with any other.

Life cycle assessment has a reputation for being either authoritative or arbitrary depending on who is describing it. Both readings come from the same source: the standard fixes how a study is conducted, not what it must conclude.

ISO 14040 sets the principles and framework; ISO 14044 sets the requirements. Understanding the four phases makes clear which parts are method and which are judgement, and therefore where to look when reading somebody else’s numbers.

Phase one decides the answer

Goal and scope definition sounds procedural and is the phase with the greatest influence on the result. It fixes the functional unit, the system boundary, the allocation approach and what is excluded.

The functional unit deserves particular attention because it is the basis of every comparison. Assessing per item, per kilogram, or per year of delivered service produces different rankings between the same two products, and all three can be defensible.

How the functional unit changes which product appears preferable
Functional unitFavoursReasonable when
One itemThe lighter or simpler productProducts are directly substitutable one for one
One kilogramThe denser productThe material itself is the subject
One year of serviceThe more durable productLifetimes differ materially
One functional outcomeThe more efficient productProducts deliver the same result differently
How the functional unit changes which product appears preferable

Phase two is where the work is

Inventory analysis compiles the inputs and outputs across the system boundary — energy, materials, emissions, waste. It is the longest phase and the one that determines data quality.

Every inventory mixes primary data measured from actual operations with secondary data from background databases. The ratio is a quality indicator that studies rarely publish and readers rarely ask for, despite it being the single best predictor of how much the result would move under scrutiny.

Replacing a background average with a supplier-specific figure commonly moves a product result by tens of per cent, because averages describe a global production mix rather than the specific supplier you buy from.

Phase three converts flows into impacts

Impact assessment translates inventory flows into environmental categories: climate change, acidification, eutrophication, resource depletion and others. This is where characterisation factors enter, and where method choice shows.

  • Category selection. A study reporting only climate change may be hiding a trade-off where the lower-carbon option is worse on water or toxicity.
  • Characterisation method. Different methods assign different factors to the same flow, so results are not portable between methods.
  • Normalisation and weighting. Optional under ISO 14044 and inherently value-laden, which is why comparative assertions disclosed to the public face additional requirements.

The single-category study is the most common trap in practice. Carbon has become shorthand for environmental performance, and a product optimised for carbon alone can perform worse across categories that were simply not reported.

Phase four is where honesty shows

Interpretation identifies significant issues, evaluates completeness and consistency, and states limitations. It is the phase most often reduced to a summary slide.

A sensitivity analysis belongs here and is the most useful part of any study for a reader. It shows how much the conclusion moves when a contested assumption changes, which is precisely the question a sceptical reader has.

Phase one constrains everything after it, which is why it is where scrutiny belongs.

How to read someone else’s study

Four questions expose most of what a summary omits, and all four are answerable from a properly reported study.

What is the functional unit, and would a different one reverse the conclusion. What share of the inventory is primary data. Which impact categories were assessed, and which were assessed and not reported. Was the study critically reviewed, which ISO 14044 requires for comparative assertions disclosed publicly.

A study that cannot answer these is not necessarily wrong. It is unverifiable, which for a claim intended to influence a purchasing decision amounts to the same thing.

Where LCA meets the passport

A passport does not perform an assessment. It records the resulting figure together with the method behind it, so a reader can tell whether two figures are comparable.

That is a more useful role than it sounds. The recurring failure in supply chain carbon data is not that figures are wrong but that incompatible figures are aggregated, and a passport that carries the boundary and functional unit alongside the number is what allows a receiving system to detect the incompatibility rather than silently summing it.

Frequently asked questions

What do ISO 14040 and 14044 actually standardise?

The method, not the answer. ISO 14040 sets principles and the framework, ISO 14044 sets requirements for conducting a study. Both leave the practitioner to choose functional unit, boundary and allocation, which is why two fully compliant studies of the same product can reach different conclusions.

What is a functional unit and why does it matter?

The basis a study is expressed per — one item, one kilogram, one year of service. It determines what can be compared, and choosing between them can reverse which of two products appears preferable. It is the first thing to check in any study and the most commonly omitted from summaries.

Is a carbon footprint the same as an LCA?

No. A product carbon footprint assesses a single impact category — climate change — using life cycle methods. A full assessment covers multiple categories, which is what reveals trade-offs where a lower-carbon option performs worse on water use, toxicity or resource depletion.

How much does primary data matter?

Considerably. Background database figures describe an average production mix rather than your specific supplier, and replacing an average with supplier-specific data commonly moves a product result by tens of per cent. The share of primary data is the best available proxy for study robustness.

Does an LCA need critical review?

ISO 14044 requires it for comparative assertions intended to be disclosed to the public. For internal studies it is optional. Where a study underpins a public comparison and has not been reviewed, that is worth knowing before the claim is repeated downstream.

Why do two studies of the same product disagree?

Usually because of scope decisions rather than data errors: different boundaries, functional units, allocation approaches or impact assessment methods. All four can be fully compliant with the standard. Comparing conclusions without first comparing those four choices is the most common misuse of assessment results in procurement.

How does an LCA relate to an EPD?

An environmental product declaration is a standardised, third-party verified summary of assessment results, published to a programme operator’s rules. The declaration constrains the choices a study would otherwise make freely, which is what makes declarations within one programme comparable with each other.

Sources

  1. GHG Protocol Product Life Cycle Accounting and Reporting StandardWorld Resources Institute and WBCSD, 2011
  2. Regulation (EU) 2024/1781 establishing a framework for ecodesign requirementsEUR-Lex, European Union, 2024-06

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