Lesson 2.2Lesson 2.2 · Life-Cycle Assessment (LCA)
Boundaries, Stages & the Functional Unit
The same building can carry two utterly different carbon numbers, both honest, simply because of where the assessment drew its edges and what it measured impact per - so before you compare any two figures you have to check they were counted the same way
'This concrete is 200 kg of CO2.' Per what? Counted from where to where? Until you answer those, the number tells you nothing - and might be hiding half the building's carbon.
In 2.1 you met the four phases of an LCA and learned that the goal-and-scope phase, done first, decides what the whole assessment means. This lesson zooms into the three scoping decisions that do the most damage when they are ignored: the system boundary (how much of the life you count), the life-cycle stages (the standard modules the life is broken into), and the functional unit (the precise thing you measure impact per, over how long). Get these straight and carbon numbers become comparable and useful. Get them muddled - or, more often, quote a number with them stripped off - and you can "prove" almost anything.
This matters because the most common carbon mistake in practice is not bad arithmetic; it is comparing figures that were never comparable. One product's declaration counts only the factory (cradle-to-gate); another counts the whole life including replacement and disposal (cradle-to-grave). One building's number is per square metre over 60 years; another is over 100. Line them up as if they were the same and you will make a confidently wrong decision. The discipline this lesson builds - always check the boundary, the stages and the functional unit before you compare - is the single habit that protects you from being fooled, including by your own good intentions.
Per what? From where to where? Over how long? Three questions that decide whether a carbon comparison means anything.
The life-cycle stages - the standard modules A to D
To count a building's carbon consistently, the industry breaks its whole life into standard stages, and knowing them by name is basic carbon fluency. Under the European building standard EN 15978 - the method most whole-life work follows - the life is divided into lettered modules. The product stage (A1-A3) covers raw material supply, transport to the factory and manufacture; this is the core of a material's embodied carbon and what most EPDs report. The construction stage (A4-A5) adds transport to site and the construction/installation process, including site energy and material wastage. Together, A1-A5 make up the up-front carbon - the emissions spent before anyone occupies the building, the irreversible burst this course keeps returning to.
The use stage (B1-B7) then spans the decades of occupation. It splits into the embodied side - B1 (in-use emissions from the fabric, such as refrigerant leaks), B2 maintenance, B3 repair, B4 replacement of components as they wear out, B5 refurbishment - and the operational side - B6 operational energy use and B7 operational water use. B4 replacement matters enormously for interiors and finishes, which are swapped many times over a structure's life, so a short-lived material's carbon is effectively multiplied. The end-of-life stage (C1-C4) covers demolition, transport, waste processing and disposal. Finally, module D sits outside the system boundary as a separate figure: the potential benefits (or loads) beyond the life - recycling, reuse or energy recovery that displaces future production. D is reported separately precisely so it is not netted off to flatter a headline number.
Why insist on this lettered scaffolding? Because it lets everyone count the same things in the same slots, so that assessments and EPDs can be added up and compared module by module. When you see "A1-A3" on a product declaration, you know exactly what it includes and, crucially, what it leaves out (transport to your site, installation, replacement, disposal). The modules are the shared language of building carbon - and most misleading comparisons come from people quoting different modules as if they were the same total.
A1-A5 = up-front carbon (irreversible); B = use (incl. B6 operational + B4 replacement); C = end of life; D = beyond, reported separately.
System boundaries - cradle-to-gate vs cradle-to-grave
The system boundary is the decision about which of those stages you actually include - where you start counting and where you stop - and it is the biggest single reason two honest carbon numbers can differ. A handful of standard boundaries recur, and you must be able to name them. Cradle-to-gate (A1-A3) counts from raw-material extraction to the factory gate - the material as made, before it leaves the plant. It is the most common boundary for product EPDs because it is what a manufacturer can control and declare, but it deliberately excludes everything after the gate: getting to your site, installing it, maintaining and replacing it, and disposing of it.
Cradle-to-gate-with-options adds selected later modules (often A4-A5, sometimes end of life). Cradle-to-grave counts the whole life, A1 through C4 - extraction to final disposal - and is the boundary a proper whole-life carbon assessment needs, because only then are you comparing the full consequence of a choice. Cradle-to-cradle goes further, crediting the material's next life through recycling or reuse (closely related to module D and to circular-economy thinking). A fifth, gate-to-gate, isolates a single process step. The point is not to memorise a glossary but to grasp that each boundary answers a different question, and a number is only interpretable once you know which one it used.
Here is where the danger lives. A cradle-to-gate figure for one product and a cradle-to-grave figure for another are not comparable - the second counts a whole life the first ignores - yet they are constantly placed side by side, sometimes innocently, sometimes to flatter a favoured option. A material can win at the gate and lose over the grave (because it wears out and needs replacing), or vice versa. This is also how greenwash hides: quote the flattering boundary, omit the rest, and let the reader assume it is the whole story. The professional reflex is simple and non-negotiable - before comparing any two carbon figures, confirm they share the same boundary and cover the same modules. If they do not, the comparison is invalid until they are put on the same basis, which is exactly the kind of work you defer to a specialist and the standards.
The functional unit - impact per what, for how long
Even with matching stages and boundaries, a carbon figure is meaningless until you know what it is measured *per*. That is the job of the functional unit: the precise, quantified description of the function being delivered, against which all impacts are normalised. "200 kg CO2e" is not an answer; "200 kg CO2e per square metre of external wall providing a specified thermal performance and fire rating for a 60-year service life" is. The functional unit forces a fair comparison by pinning down not just the amount but the *job*: two wall systems can only be compared if they deliver the same function - the same performance, for the same duration. Compare per kilogram and you will favour dense materials unfairly; compare per unit of function and you compare like with like.
For construction products specifically, EPDs often use a declared unit (for example, per kilogram or per cubic metre of product) rather than a full functional unit, precisely because the manufacturer cannot know how much of the product your design will use or how long it must last. That is legitimate, but it throws the burden onto you: a declared-unit figure must be scaled by the quantity your design actually uses and, where relevant, by how often the product is replaced, before it becomes a meaningful contribution to your building. Reading "per kg" as "per project" is a classic error.
Inseparable from the functional unit is the reference study period - the length of time the assessment considers, typically 50 or 60 years for a building, though it varies. It matters because the study period governs how many times replaceable components (B4) are counted, how much operational carbon (B6) accumulates, and therefore the whole balance between up-front and lifetime emissions. Two identical buildings assessed over 50 versus 100 years will report very different totals, and neither is "wrong" - they answer different questions. So the rule that closes this lesson is a compound one: a carbon figure is only comparable when the stages, the boundary, the functional unit *and* the reference study period all match. Miss any one and you may be comparing apples with orchards. This is why credible comparisons are done to a common standard by someone who controls all four - and why your first question of any number is always "per what, from where to where, over how long?"
Putting it to work - and where to defer
How does this discipline change what you actually do? First, it makes you a sharper reader. Handed a carbon claim - by a manufacturer, a competitor's case study, a rating submission - your reflex becomes to find the four edges before you react: which modules, which boundary, which functional or declared unit, which study period. Nine times out of ten the claim is fine but partial (cradle-to-gate only, say); occasionally it is misleading; either way you now know what it does and does not prove. That single habit will save you from more bad decisions than any amount of material trivia.
Second, it makes you a better briefer of assessments. When you commission a whole-life carbon assessment (2.4), you - with the specialist - set the goal and scope: you agree the boundary (usually cradle-to-grave for a real building decision), the reference study period, and the functional unit, up front, so the result answers your actual question and can be compared against benchmarks that use the same basis. An assessment scoped loosely produces a number that cannot be benchmarked or trusted; an assessment scoped tightly and transparently produces one that can. Agreeing these edges is a five-minute conversation that determines whether the whole exercise is worth anything.
Third, it keeps you honest. Because you understand that the boundary makes the number, you will resist the temptation - subtle and common - to quote the flattering scope for your own project. If your building's up-front carbon (A1-A5) is high, you do not bury it by only ever reporting a cradle-to-gate product figure; you report on the agreed whole-life basis and let the number stand. The standards (EN 15978 for buildings, EN 15804 for products) exist precisely to fix these edges so that everyone counts the same way, and the reason binding assessments go to a qualified specialist is that getting the boundaries, modules, units and period consistent - and defensible against a benchmark - is exacting work. Your role is to understand the edges well enough to demand they be set properly and read honestly. That is what turns "it depends" from an excuse into a discipline.
EN 15978 (life-cycle modules A-D)
The standard staging of a building's life for assessment
Defines A1-A3 product, A4-A5 construction, B1-B7 use, C1-C4 end of life and D beyond-the-boundary. Learn the modules; the binding module split follows the standard and a specialist.
System boundary (cradle-to-gate vs cradle-to-grave)
How much of the life an assessment counts
A number is only interpretable against its boundary. Never compare a cradle-to-gate figure with a cradle-to-grave one; put both on the same basis first.
Functional unit & reference study period
Impact 'per what', over how long
Comparisons require the same function and the same study period (often 50-60 years). EPDs' declared units must be scaled by quantity and replacement before use.
Workshop - stress-test a comparison for matching edges
This workshop trains the reflex that protects you most: checking whether a comparison is even valid. You will take two carbon figures - real or from a case study - and test whether their stages, boundary, functional unit and study period actually match before drawing any conclusion.
Two carbon figures for similar items (published EPDs or a case study are ideal) and a notebook. No calculation required - this is about testing comparability.
Goal: to judge whether a carbon comparison is valid, not just which number is lower Inputs: two carbon figures for similar products/elements (from EPDs, a case study, or a manufacturer claim) + this lesson Time: ~40 minutes
- 1For each figure, write down its life-cycle stages/modules (is it A1-A3 only, or A1-C4, or something else?). Flag any mismatch immediately.
- 2For each figure, write down its system boundary in plain words - cradle-to-gate, cradle-to-grave, or with-options - and note what each one excludes.
- 3For each figure, write down the functional or declared unit (per kg, per m2, per m2 for how many years?) and the reference study period. Note whether they match.
- 4Decide: given the four edges, is this comparison valid as it stands? If not, state exactly what would have to be aligned to make it fair (e.g. 'scale the per-kg figure by quantity and add replacement over 60 years').
- 5Write a one-line verdict you could defend to a client: what the comparison does and does not prove, and that any binding version needs a specialist to put both on a common standard.
You’ll walk away with
A one-page 'edges check' on a real comparison: the stages, boundary, functional unit and study period of each figure, a validity verdict, and what would be needed to make the comparison honest. This is a reusable filter for every carbon comparison you meet.
Three altitudes on the same idea
Read the band that fits you — or all three.
You set the scope of every carbon conversation on your project, so you must own the edges. When you brief a whole-life carbon assessment, insist on cradle-to-grave (A1-C4, with D reported separately), a clear reference study period, and a functional unit tied to the building's actual function - then hold every later comparison to that same basis. Watch two traps in particular: comparing a product's A1-A3 figure to another's whole-life figure, and letting a long study period quietly dilute a high up-front carbon that your design is actually responsible for. Report up-front carbon (A1-A5) honestly as its own line, because that is the irreversible carbon your design controls. Defer the binding module-by-module numbers to the specialist and EN 15978.
Your domain lives in module B4 - replacement - and that is where boundary thinking pays off most. Interiors and finishes are swapped many times over a building's life, so a material's carbon over a 60-year study period can be several times its single-installation figure; a cheap-at-the-gate finish that fails early can lose badly on a whole-life boundary. When you read a product EPD, note that it is usually a declared unit (per kg or per m2) at a cradle-to-gate boundary - you must scale it by the quantity you use and by how many times it will be replaced before it means anything for the project. Specify for durability and reuse, and compare finishes only on a matching functional unit and study period, coordinating binding numbers with the assessor.
Memorise the modules and the boundaries - this is examinable, quotable, and the fastest way to sound (and be) carbon-literate. Learn that A1-A3 is the product stage, A4-A5 gets it to site and installed, A1-A5 together are up-front carbon, B covers use (B4 replacement and B6 operational energy especially), C is end of life, and D sits outside the boundary, reported separately. Learn cradle-to-gate versus cradle-to-grave cold. Then practise the one habit that matters: whenever you see a carbon number, ask 'per what, from where to where, over how long?' - functional unit, boundary, study period. Getting into that reflex now will make every later module, and every EPD you ever read, far easier.
“If two carbon figures are both given in kg CO2e, they are measuring the same thing and can be compared directly - a lower number is simply better.”
Do it yourself
No tools needed - reason it through.
- 1Name the life-cycle stages A1-A3, A4-A5, B, C and D in your own words, and say which of them make up 'up-front carbon'.
- 2Explain the difference between cradle-to-gate and cradle-to-grave, and give an example where a material wins on one and loses on the other.
- 3What is a functional unit, and why can't you fairly compare two wall systems 'per kilogram'?
- 4Why does the reference study period change a building's total carbon, and why isn't a 50-year answer 'more correct' than a 100-year one?
- 5A manufacturer quotes a low A1-A3 figure. What three questions do you ask before comparing it to a rival product?
The one line to carry out
Peer-reviewed journals & authoritative standards
- 01Functional unit — Wikipedia - Functional unit, 2026.
- 02Life-cycle assessment — Wikipedia - Life-cycle assessment, 2026.
- 03Cradle-to-cradle design — Wikipedia - Cradle-to-cradle design, 2026.
- 04Embodied energy — Wikipedia - Embodied energy, 2026.
We keep pointing to the data that fills these modules - the actual kg CO2e for real products. That data has a name and a rulebook: the Environmental Product Declaration. Next we learn to read one, and why a good assessment lives or dies by data quality.
The author
Amogh N P
Architect, interior designer, and creative polymath. Studio Matrx began in his notebooks — his vision of design made honest, useful, and open to everyone. Its Academy is written and taught in his memory, and free, forever.
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