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Last reviewed July 2026
Authored by Jeremiah Say

Lead Systems Architect at GreenCalculus. Translates GHG Protocol methodology into high-precision JavaScript calculation engines. Architect of the MasterBrain data layer covering 1,000+ environmental tools, aligned with IPCC AR6 and the GHG Protocol Corporate Standard (2026 revision).

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Automated verification pipeline that audits every page against its underlying calculation code, source documents, and MasterBrain data layer. Traces every figure cell-by-cell to its named source workbook, enforces cell-by-cell provenance attribution on every emission factor, and cross-checks methodology prose against the data layer to catch stated-vs-actual discrepancies before publication.

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Product Carbon Footprint & LCA Calculators (ISO 14067)

Two teams can footprint the same product and land on numbers that differ by a factor of two — not because either miscalculated, but because they drew the system boundary in different places and split shared emissions by different rules. A product carbon footprint is only as credible as the boundary and allocation choices behind it.

Fix those choices first, then the arithmetic is the easy part.

Quick Answer

A product carbon footprint sums the greenhouse gases across a product’s life cycle under ISO 14067. Define the boundary — cradle-to-gate stops at the factory gate, cradle-to-grave runs to disposal — and an allocation rule for shared processes. Change either and the number changes.

Where the numbers come from

Calculations follow ISO 14067 and the underlying ISO 14040/44 LCA framework, drawing on life-cycle inventory data such as the ecoinvent database. Every factor is versioned in the MasterBrain data layer, and how the numbers are built explains the framework choices — ISO 14067 vs PEF vs Pathfinder — and why they move the result.

Product carbon footprint and LCA topic hub — two mini-hubs (sector footprints; methods and boundaries) spanning eleven calculators, aligned to ISO 14067 and ISO 14040/14044.
Aligned to ISO 14067

Boundaries — cradle-to-gate vs cradle-to-grave

The system boundary is the first decision in any product footprint, and it changes the number more than the arithmetic does. Cradle-to-gate covers raw material extraction, transport and manufacture up to the point the product leaves the factory — the boundary most business-to-business footprints and supplier declarations use. Cradle-to-grave extends that to distribution, use and end-of-life, the full picture a consumer-facing claim needs.

Neither is more correct; they answer different questions, and a footprint quoted without stating its boundary is unreadable. A cradle-to-gate figure for a component is exactly what a downstream manufacturer needs to slot into their own assessment; a cradle-to-grave figure is what you need to compare two finished products a customer will actually use and discard. The cradle-to-gate calculator and the cradle-to-grave calculator build each under ISO 14067.

State the functional unit too

A footprint is always per functional unit — one litre of paint covering a defined area, one garment worn a defined number of times — not per kilogram of product. Two products only compare fairly on the same functional unit and the same boundary. Get these two declarations right and most “the numbers don’t match” disputes disappear.

Pick your PCF calculator

Building a footprint from scratch, testing a method choice, or starting from a sector template? Go straight to the calculator.

Two sub-topic hubs split method from sector: PCF methods & boundaries (ISO 14067, allocation, frameworks) and sector product footprints (food, apparel, electronics, packaging).

Cradle-to-gate PCF →

Factory-gate footprint under ISO 14067.

Food footprint →

Sector template for food products.

Cradle-to-grave PCF →

Full life cycle to end-of-life.

Allocation methods →

Split shared emissions between co-products.

Sensitivity & hotspots →

Find what drives and swings the result.

Framework comparison →

ISO 14067 vs PEF vs Pathfinder.

Packaging footprint →

Sector template for packaging.

Apparel & textile →

Sector template for garments and textiles.

Electronics footprint →

Sector template for electronic goods.

Beverages footprint →

Sector template for drinks products.

Construction materials →

Sector template for building materials.

Which PCF calculator do I need?

Build from scratch, interrogate a method, or start from a sector template — the answer decides the tool. This table maps each calculator to what it does and when to reach for it.

What you’re doing Calculator Basis When to use it Methodology
Factory-gate footprint Cradle-to-gate PCF ISO 14067, A1–gate B2B declarations, component footprints, supplier data Cradle-to-gate PCF methodology
Full life-cycle footprint Cradle-to-grave PCF ISO 14067, full life cycle Consumer-facing claims, product comparisons Cradle-to-grave PCF methodology
Splitting shared emissions Allocation methods Economic / physical / system expansion Co-products, multi-output processes, recycled content Allocation methods methodology
Finding the drivers Sensitivity & hotspots Contribution + sensitivity analysis Prioritising reductions, testing assumptions Sensitivity & hotspot methodology
Choosing a framework Framework comparison ISO 14067 vs PEF vs Pathfinder Deciding which rulebook to report under Frameworks comparison methodology
Food product Food footprint Sector template A fast, credible food-product first pass Food PCF methodology
Packaging Packaging footprint Sector template Packaging formats and materials Packaging PCF methodology
Garments & textiles Apparel & textile Sector template Clothing and textile products Apparel & textile PCF methodology
Electronic goods Electronics footprint Sector template Devices and electronic components Electronics PCF methodology
Drinks Beverages footprint Sector template Beverage products and their packaging Beverages PCF methodology
Building materials Construction materials Sector template Product-level material footprints (see embodied-carbon hub for buildings)

What each calculator covers

The cluster splits into three jobs: building a footprint under the core standard, interrogating the method choices that determine its credibility, and starting from a sector template when you want a fast, defensible first pass. Each calculator carries the boundary rules and factor set for one of those jobs.

Building the footprint — ISO 14067 cradle-to-gate & cradle-to-grave

The cradle-to-gate PCF calculator is the workhorse and the hero of this cluster: it builds a product footprint from material and process inputs up to the factory gate, under ISO 14067 (methodology). It is the right starting point for a business-to-business declaration or a component figure someone downstream will build on. The cradle-to-grave calculator extends the same boundary through distribution, use and end-of-life for a full life-cycle result (methodology) — the version a consumer-facing claim or a like-for-like product comparison needs.

Interrogating the method — allocation, sensitivity & framework choice

Three calculators address the decisions that separate a credible footprint from an arguable one. The allocation methods calculator handles the hardest of them — how to split emissions from a shared process across its co-products, by economic value, physical property or system expansion — since the choice can swing a result substantially (methodology). The sensitivity and hotspot calculator identifies which inputs dominate the total and which assumptions the result is most sensitive to, so reduction effort lands where it matters (methodology). The frameworks comparison calculator sets ISO 14067 against the EU’s Product Environmental Footprint and the WBCSD Pathfinder rules, so you can see how the rulebook you report under shapes the number (methodology).

Sector templates — food, packaging, apparel, electronics, beverages, construction

Six calculators start you from a sector-specific template rather than a blank inventory, each pre-loaded with the processes and factors typical of that product class. The food footprint calculator is the second hero — food footprints lean heavily on agricultural life-cycle data such as the Poore & Nemecek dataset (methodology). Alongside it sit templates for packaging (methodology), apparel and textiles (methodology), electronics (methodology), beverages (methodology), and construction materials. The construction-materials template overlaps the embodied-carbon cluster — it produces a product-level material footprint, where the whole-building side lives in the embodied carbon calculators hub.

Allocation — the choice that moves the number

Allocation is the question that causes the most product-footprint disputes, so it is worth stating plainly. When one process produces more than one useful output — a dairy yielding milk and cream, a refinery yielding several fuels, a mill yielding grain and bran — the emissions have to be divided among them, and there is no single physically correct way to do it. The three recognised approaches give different answers: economic allocation splits by the market value of each co-product, physical allocation splits by a physical property such as mass or energy content, and system expansion credits a co-product with the emissions it displaces elsewhere.

ISO 14040/44 sets a hierarchy — avoid allocation by subdivision or system expansion where you can, then allocate by a physical relationship, then by economic value as a last resort — but real products rarely allow the cleanest option, so the choice is often unavoidable and always consequential. The honest position is that the allocation method is a reported assumption, not a hidden one: two footprints are only comparable if they used the same method, and a result quoted without naming its allocation basis is incomplete. Recycled content raises the same question in a sharper form, since the credit for recycling can be assigned to the product that supplies the scrap or the one that uses it, but not both.

Name the boundary, functional unit and allocation basis

A product footprint is only comparable to another when all three match: the system boundary, the functional unit, and the allocation method. Change any one and the numbers stop being like-for-like. Report all three alongside the figure — a headline number without them cannot be verified or fairly compared.

How the numbers are built

Every calculator here follows the same chain — life-cycle inventory (the material and energy flows of each process) multiplied by characterisation factors that convert each greenhouse gas to carbon dioxide equivalent using its global warming potential. The framework sits on ISO 14067 over the ISO 14040/44 LCA method, with EPD-style declarations governed by ISO 14025; inventory data draws on sources such as the ecoinvent database and, for food, the Poore & Nemecek dataset. Where only spend data is available rather than physical inventory, the sector templates fall back to environmentally-extended input-output factors — the same MRIO basis a spend-based screen uses.

The single biggest driver of a PCF number is the boundary — where the assessment starts and stops. ISO 14067 splits the life cycle into these stages, and the two boundary calculators differ only in where they draw the line:

ISO 14067 life-cycle stages, and which are inside a cradle-to-gate vs a cradle-to-grave boundary.
Life-cycle stageCradle-to-gateCradle-to-grave
Raw material acquisition
Production / manufacturing
Distribution & storage
Use phase
End of life

A cradle-to-gate figure ends at the factory gate — right for comparing suppliers or feeding a downstream assembler. A cradle-to-grave figure adds distribution, use and disposal, which for energy-using products often dominate. Comparing a gate figure against a grave figure is the most common PCF error.

The framework you report under is itself a provenance choice. ISO 14067, the EU Product Environmental Footprint and the WBCSD Pathfinder rules differ on allocation defaults, biogenic-carbon treatment and required boundaries, so the same product can carry different published figures under each — legitimately. Each calculator states the framework and factors it applied, and every value is versioned and traceable in the MasterBrain data layer, so you can see which dataset and vintage produced a number. Each calculator has a matching methodology page setting out its boundaries and assumptions.

Underneath every PCF is one universal step: each greenhouse gas is converted to CO₂-equivalent by its global warming potential. Those characterisation factors are read live from the data layer at MasterBrain v2026.110 (IPCC AR6, 100-year):

GWP-100 characterisation factors every PCF applies, read live from the MasterBrain (IPCC AR6 WGI, Table 7.SM.7).
Greenhouse gasGWP-100 (AR6)
Carbon dioxide (CO₂)1
Methane, fossil (CH₄)29.8
Nitrous oxide (N₂O)273
HFC-134a (refrigerant)1530
Sulphur hexafluoride (SF₆)25200
Why a gram of the wrong gas dwarfs a kilo of CO₂

A kilogram of SF₆ carries the same 100-year warming as roughly 25 tonnes of CO₂; a kilogram of HFC-134a, about 1.5 tonnes. In a PCF this is why refrigerant leaks, foam-blowing agents and process gases can outweigh a product’s entire energy footprint — the mass is tiny, but the characterisation factor is enormous. Getting the gas inventory right matters as much as getting the energy right.

After your first number

A product footprint feeds outward in two directions. Upstream, it becomes a line in a corporate inventory — a supplier’s product footprint is a buyer’s Scope 3 Category 1 purchased-goods emission, which is where the spend-based screening in the wider inventory clusters hands off to primary product data. Downstream, a credible footprint underpins a product claim, an EPD, or a reduction target on the product itself. The related embodied carbon calculators hub shares the same LCA standards pool for building materials and whole buildings, and its construction-materials work overlaps the sector template here.

If you are working at organisation rather than product level, the organizational & sector footprint calculators give a whole-entity baseline, and the full carbon calculator directory covers every source-level tool an inventory draws on.

Start with the boundary most product footprints lead with — cradle-to-gate under ISO 14067 — or start from a sector template if you want a fast, credible first pass for food, packaging, apparel, electronics or beverages.

Define the functional unit and system boundary, build a life-cycle inventory of the material and energy flows across that boundary, and multiply each by its emission factor to convert to CO₂e. The cradle-to-gate calculator does this up to the factory gate under ISO 14067; the cradle-to-grave version extends it to disposal. The boundary and the allocation rule for shared processes matter more than the arithmetic — set those first, and state them alongside the result.

Cradle-to-gate covers raw material extraction, transport and manufacture up to the point the product leaves the factory. Cradle-to-grave extends that to distribution, use and end-of-life — the full life cycle. Business-to-business declarations and component footprints usually use cradle-to-gate, because a downstream manufacturer adds the later stages themselves. Consumer-facing claims and finished-product comparisons need cradle-to-grave. Neither is more correct; they answer different questions, and a footprint is unreadable without stating which boundary it used.

ISO 14040/44 sets a hierarchy: avoid allocation by subdividing the process or using system expansion where you can, then allocate by a physical relationship such as mass or energy, and use economic value only as a last resort. In practice most multi-output processes force a choice. Whichever you use, it is a reported assumption — two footprints only compare if they used the same method, so name the allocation basis alongside the result rather than burying it.

ISO 14067 is the international standard for product carbon footprints and the usual default. The EU Product Environmental Footprint (PEF) is the European Commission’s method, prescriptive on datasets and required for some EU contexts. The WBCSD Pathfinder framework targets consistent, exchangeable footprints across supply chains. They differ on allocation defaults, biogenic-carbon treatment and boundaries, so the same product can carry different figures under each — legitimately. Choose by who you report to; the frameworks comparison calculator shows the effect of switching.

From life-cycle inventory databases. The calculators draw on sources such as ecoinvent for general processes and the Poore & Nemecek dataset for food, all versioned in the MasterBrain data layer so each figure traces to a dataset and vintage. Where only spend data is available, the sector templates fall back to environmentally-extended input-output factors — lower resolution than primary data, but a defensible screen. Primary supplier data always beats a database average where you can get it.

A functional unit is the quantified service a product delivers — one litre of paint covering a set area, one garment worn a set number of times — and every footprint is expressed per functional unit, not per kilogram. It matters because it is the only fair basis for comparison: a paint that weighs less per litre but covers less area may be worse per unit of coverage. Two products only compare on the same functional unit and the same system boundary.

Not quite. A product carbon footprint quantifies greenhouse-gas emissions under ISO 14067. An Environmental Product Declaration is a broader, third-party-verified report of a product’s environmental impacts — including carbon but also water, resource use and others — drawn up under ISO 14025 to defined product category rules. A PCF can feed an EPD, and both rest on the same underlying ISO 14040/44 life-cycle assessment, but an EPD is the verified declaration format, not just the carbon number.

Yes. Every calculator in this hub is free to use and shows the standard and factor source behind its result. Each produces a defensible estimate against named LCA standards — suitable for internal decisions, supplier screening and a first credible footprint — not a substitute for a third-party-verified, critically reviewed study where a claim or disclosure regime requires one. The methodology page for each calculator sets out its boundaries and assumptions.

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