Product carbon footprint
2026 01 26
•
5 MIN
Carolina Skarupa
Product Carbon Footprint Analyst

Defining the boundaries of a Life Cycle Assessment (LCA) is the single decision that most determines the reliability of the study, its usefulness for decision-making, and its validity for audits and reporting. Before choosing emission factors or software, you must decide which life cycle stages fall inside the analysis and which are left out.
The two most widely used boundaries are cradle to gate and cradle to grave. This article explains what each one covers, when to use them, and how to justify your choice based on the purpose of the study, the type of product, the sector, and reporting requirements (carbon footprint, eco-design, environmental declarations, CSRD).
Defining the system boundaries of a Life Cycle Assessment means determining which stages are included in the analysis and which are excluded. That boundary sets the technical perimeter of the study and directly shapes the results: the ISO 14040 and ISO 14044 standards do not impose a specific boundary, but they do require you to define and justify it transparently.
A poorly defined boundary produces incomplete impacts, non-comparable results, and flawed conclusions. A well-justified one allows you to make sound decisions, defend the study under critical review, and connect the LCA with ESG metrics.
In practice, the choice of boundaries determines:
A cradle-to-gate LCA analyses environmental impacts from raw material extraction to the point where the product leaves the production process. The analysis stops at the factory gate.
This approach includes the upstream activities needed to manufacture the product: sourcing and processing of materials, intermediate transport, and internal industrial processes. By contrast, it excludes distribution to the final customer, the use phase, and end of life. By focusing on what the manufacturer directly controls, it reduces uncertainty and improves the traceability of the data.
It is the right choice when the product analysed is not a final good, but a component, material, or ingredient that is integrated into a larger system. It is also the usual approach when the objective is to:
Its main strength is methodological robustness: by sticking to processes controlled by the organisation, it reduces dependence on external assumptions. This translates into lower data complexity, greater reproducibility, lower uncertainty, lower cost, and simpler auditing.
Its limitation is clear: it does not allow you to assess the total environmental impact of the product, because it excludes stages that often concentrate most of the impact. It is insufficient when the main impact occurs during use, when energy consumption in use is high, when end of life shapes the balance (recycling or reuse), or when you want to compare final products. A cradle-to-gate study does not let you claim that a product is “more sustainable” in absolute terms, only that its production process is more efficient.
A cradle-to-grave LCA analyses the full life cycle, from raw material extraction to final disposal. In addition to production, it incorporates distribution, the use phase, maintenance, and end-of-life scenarios. It is the most complete analysis and the one that offers a systemic view of the product.
Technically, it requires modelling use behaviours, logistics scenarios, and end-of-life options, which increases complexity. One variant is cradle to cradle, which assumes that materials are reincorporated into a new cycle instead of ending up as waste.
It is necessary when:
Its main value is identifying hidden impacts that do not appear in an analysis limited to production, and uncovering real improvement opportunities in design, durability, energy efficiency, and end of life. Its main risk is dependence on assumptions: unrepresentative usage patterns, unrealistic recycling rates, or unjustified transport scenarios can compromise the validity of the study. That is why a broad LCA without solid data is usually worse than a more limited but methodologically robust one.
In the construction sector, the LCA boundary is expressed through the modules of the EN 15804+A2 standard, which is the basis for EPDs of construction products:
Since the EN 15804+A2 revision, the minimum scope of a construction EPD is no longer just A1-A3; it usually also requires C1-C4 and D, bringing sector practice closer to the logic of cradle to grave. You can go deeper in the LCA guide for construction and in how to calculate the carbon footprint of construction materials.
The choice should always start from the objective of the study. There is no universally better approach, only the one that suits each decision. A simple practical rule: if a significant share of the impact occurs outside the factory (in use or at end of life), cradle to gate falls short and you should extend to cradle to grave.
The second criterion is the organisation's real capacity to collect reliable data at each stage. An efficient strategy is to start with a narrow, well-measured scope and expand it progressively as use and end-of-life data become available. Management platforms such as Manglai's product footprint help structure that calculation and connect it with the product carbon footprint.
The CSRD requires consistency between strategy, risks, metrics, and targets. A poorly defined LCA boundary generates inconsistent indicators and weakens the ESG narrative. Conversely, a well-scoped and documented LCA lets you build defensible KPIs, reduce the risk of greenwashing, and connect environmental impact to decision-making.
Choosing between cradle to gate and cradle to grave is a strategic decision, not a formality. Organisations that master LCA first define the objective, set boundaries rigorously, document assumptions, and expand the analysis progressively. A well-defined LCA reduces risk, improves decisions, and strengthens ESG credibility.
No. The better LCA is the one that precisely answers the defined objective. For an intermediate material, cradle to gate is usually more rigorous and useful.
Yes. It is the most efficient strategy and the one most commonly used by organisations with some maturity in measurement.
No. ISO 14040 and ISO 14044 require you to justify the system boundary; they do not impose a specific one.
The broader the scope you communicate, the greater the demand for transparency and rigour. Communicating a cradle-to-gate result as if it were the product's total impact is a greenwashing practice that should be avoided.
Carolina Skarupa
Product Carbon Footprint Analyst
About the author
Graduated in Industrial Engineering and Management from the Karlsruhe Institute of Technology, with a master’s degree in Environmental Management and Conservation from the University of Cádiz. I'm a Product Carbon Footprint Analyst at Manglai, advising clients on measuring their carbon footprint. I specialize in developing programs aimed at the Sustainable Development Goals for companies. My commitment to environmental preservation is key to the implementation of action plans within the corporate sector.
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