Haute Lumière
Commerce · IV.01 · MMXXVI · daylight
One page each. A reader who reads only these ten pages has the chapter.
The idea. A manufacture is net positive with respect to an impact category when, over a declared boundary, against a declared baseline, compared with a declared counterfactual, and expressed per declared functional unit, the total carries a negative sign — the system removes more of that impact than it adds.
Four declarations. Every one of them is a choice somebody makes, and every one of them can move the answer past zero.
Worked example. One square metre of commercial carpet tile, from a third-party verified declaration. Counted at the factory gate with its biogenic credit and a bio-loaded backing: −0.30 kg CO₂e/m² — negative. Counted over the same product's own fifteen-year service life with an incineration end of life: +11.325 kg CO₂e/m². Same object, same physics, 11.625 kg apart, and a change of sign.
Why it matters. "Net positive" is not a property of a product. It is a property of a sentence about a product, and the sentence has four adjustable parts. Once you know which four, you can read anybody's claim in about ninety seconds — and write your own so that it survives being read.
You already know this because you have seen a project come in under budget by moving what counted as the project.
The idea. ISO 14040 asks for the functional unit: the quantified performance the product delivers, used as the reference for everything else. Not the product. The performance, for a stated time.
The difference is the whole discipline. A kilogram of carpet is a mass. A square metre of floor covering, held for fifteen years, is a function — and it is the only thing two different products can honestly be compared on.
Worked example. The declaration for the tile in this chapter states: functional unit 1 m², nominal mass 3.34 kg, reference service life 15 years. Now compare two tiles by mass and the heavier one loses. Compare them by square metre per year of service and a tile that lasts twenty years beats one that lasts eight even if it weighs more — which is the correct answer and the one the mass comparison cannot reach.
Why it matters. Almost every misleading product comparison you will meet is a unit problem rather than a data problem. The numbers are right. They are answers to two different questions.
You already know this because you have compared two jobs by salary and then remembered the hours.
The idea. The boundary says which processes are inside the study. In construction EPDs it is written as modules, and the letters are worth learning once: A1–A3 product stage (raw materials, transport to the factory, manufacture), A4–A5 transport to site and installation, B1–B7 the use stage including B2 maintenance, C1–C4 end of life, and D benefits and loads beyond the system boundary.
Worked example. The declared modules for one square metre, in kg CO₂e: A1–A3 2.760; A4 0.323; A5 0.238; B2 0.403; C2 0.00710; C4 0.104. Modules B1, B3, B4 and B5 are not declared and the declaration says so. Sum what is declared and you get 3.835 kg CO₂e/m².
Why it matters. "Cradle to gate" means A1–A3. "Cradle to grave" means A1–C4. They are routinely printed under the same headline adjective, and they differ here by 39 percent before you have corrected anything else.
You already know this because you have read a price that turned out to be ex-VAT, ex-delivery and ex-installation, and all three were disclosed.
The idea. Carbon that a plant pulled out of the air and that ends up inside a product is counted as a removal — a negative number — at the moment it enters the product, and as an emission whenever it is released. Whether the product is net negative therefore depends on what you assume happens at the end of its life.
Worked example. The declaration's own biogenic bookkeeping: 6.22 kg CO₂ removed into the product, 4.55 kg emitted from it during manufacture, 0.218 kg into packaging and 0.0396 kg out of it. That leaves 1.848 kg of biogenic carbon still stored in the tile when it is thrown away. The declared disposal route is 95.7 percent landfill, 4.3 percent incineration, and no recycling — and it treats the stored carbon as staying stored.
Send the same tile to an energy-from-waste plant instead, which is the normal European fate, and the 1.848 kg returns to the air.
Why it matters. The gate-stage biogenic credit is 41.9 percent of the fossil burden on this product. It is the single largest lever in bio-based design, and it is the one most dependent on an assumption about a bin.
You already know this because you know the difference between money in an account and money you have been promised.
The idea. A use-stage module is a rate. The reference service life is the multiplier. A declaration that gives you one and not the other has given you half a number, and the half it gives you is always the flattering one.
Worked example. The tile's declaration states a reference service life of 15 years, and states plainly that maintenance (B2) "is represented for one year." B2 is 0.403 kg CO₂e/m²/yr. Multiply:
0.403 x 15 = 6.045 kg CO2e/m2 over the service life
total, whole life = 9.477 kg CO2e/m2 (3.43x the cradle-to-gate figure)
And the shares invert:
as declared (1 yr) over 15 years
A1-A3 product 72.0 % 29.1 %
B2 maintenance 10.5 % 63.8 %
Why it matters. This is the chapter's central finding. Held for its own declared life, the largest climate impact of a carpet tile is the cleaning, not the carpet — and the whole industry conversation is about the 29 percent. Nothing was hidden. The sentence is in the document.
You already know this because you have compared a monthly subscription with a one-off purchase and known to multiply before deciding.
The idea. A baseline is a measured past state of the same system: what this thing was, before. A counterfactual is an unmeasured alternative present: what would have happened instead, if this thing did not exist. The first can be audited. The second cannot, because it did not occur.
Worked example. Interface reporting that its average carpet tile fell from an implied 16.77 kg CO₂e/m² to 5.2 kg CO₂e/m² — a 69 percent cut — is a baseline claim. Two measured states of the same production system, a quarter of a century apart. An auditor can test it.
A developer reporting that a wind farm "avoided 2.300 Mt CO₂e" is a counterfactual claim. There is no measurement of the world in which the wind farm was not built.
Why it matters. Both appear in the same sustainability report, in the same font, often in the same sentence. One is bookkeeping and one is a model, and the assurance a reader can place in them differs by an order of magnitude.
You already know this because "I lost four kilos" and "I would have gained four kilos" are not the same claim, and only one of them was on a scale.
The idea. Avoided emissions — sometimes called scope 4, though it is not a scope — are the difference between a low-carbon scenario and a counterfactual baseline. They are a legitimate and useful thing to report. They are not subtractable from your own inventory, and the WBCSD's 2023 guidance says so explicitly: avoided emissions are a separate ledger, not a discount on your own.
Worked example. One developer, 10.0 TWh/yr of offshore wind at the IPCC median lifecycle intensity of 12 g CO₂e/kWh. What did it displace?
coal, pulverised 820 g/kWh -> 8.080 Mt CO2e/yr avoided
gas, combined cycle 490 g/kWh -> 4.780 Mt CO2e/yr
EU-27 grid average 242 g/kWh -> 2.300 Mt CO2e/yr
onshore wind an
auction would have
built anyway 11 g/kWh -> -0.010 Mt CO2e/yr
A spread of 8.090 Mt on one wind farm, decided by one sentence chosen by the party making the claim.
Why it matters. A "net positive" produced by subtracting the fourth column from an inventory is not permitted by the standard it cites. When Interface retired its offset-based Carbon Neutral Floors programme in 2024, this is the arithmetic it was declining to keep defending.
You already know this because you would not let a supplier settle an invoice by telling you how much they saved you.
The idea. When one process makes two things, its impacts have to be split between them. ISO 14044 does not leave this to taste. It sets a hierarchy: first, avoid allocation — by subdividing the process, or by expanding the system to include the co-product's function. Second, partition by a physical relationship that reflects how the outputs change with the inputs. Third, and only then, partition by another relationship such as economic value.
Worked example. A plant makes yarn and a residue stream sold as filler. Split by mass and the yarn carries little; split by revenue and the yarn carries almost everything; expand the system to credit the filler with the virgin filler it displaces and the yarn carries something else again. All three are defensible methods. Only one order of preference is the standard's.
Why it matters. Allocation is where a product footprint is most often quietly chosen rather than computed, and the hierarchy exists precisely to narrow the room for choosing. If a declaration does not state its allocation method, that absence is the finding.
You already know this because you have seen overhead apportioned by headcount and then by revenue, and watched a division change from profitable to loss-making without anyone selling anything differently.
The idea. Divide what you pay by what you remove, and you get a price per tonne. It is the single most useful number in an environmental specification, and it is almost never printed, because it is frequently uncomfortable.
Worked example. Specify the lower-carbon tile over the 2019 average:
premium $35.00/m2 x 5.0% = $1.75/m2
carbon removed 5.2 - 2.76 = 2.44 kg CO2e/m2
implied cost 1.75 / (2.44/1000) = $717/t CO2e
Against internal carbon prices in general corporate use — $50, $100, $190, $250 a tonne — the cut is worth $0.122, $0.244, $0.464 and $0.610 per square metre. None of them clears $1.75. On carbon alone, at that premium, the specification loses.
And the comparison that rescues it: a 30 percent reduction in maintenance intensity removes 1.813 kg CO₂e/m² over the service life — 0.74× the entire gate-stage cut — at no capital cost. (A stated scenario, not a measurement; the declaration does not break B2 down.)
Why it matters. Ranking every option by implied $/t across the whole boundary is the exercise that tells you where the money should go. It usually is not where the brochure is pointing.
You already know this because you have compared two ways of saving the same hour and picked the cheaper one without needing a framework.
The idea. ISO 14044 treats one kind of claim as more dangerous than the rest: a comparative assertion disclosed to the public — a statement that this product is environmentally better than, or equivalent to, a competing product, made to a public audience. For those, critical review is not optional. It requires a panel of interested parties rather than a single friendly expert, and weighted single scores may not be presented as objective comparison.
Worked example. "Our tile is carbon negative" is a claim about one product and, read strictly, an inventory statement over a stated boundary. "Our tile is better than the alternative" is a comparative assertion, and if it appears on the website, the brochure or the sales deck it is disclosed to the public — the 2020 amendments made that scope explicit. The second sentence carries a review obligation the first does not.
Why it matters. Most organisations make comparative assertions constantly and have never once convened a panel, because they believe the obligation attaches to academic publication. It attaches to the marketing. Treating the requirement as a floor rather than a ceiling — inviting somebody with an interest in disagreeing — is the cheapest insurance available against a claim that has to be withdrawn later.
You already know this because you have watched a number survive an internal review and then fall apart the first time somebody outside the building asked where it came from.