Embodied carbon has moved from a research topic to a line item on Canadian project schedules in about five years. Developers are being asked for whole-building carbon numbers by municipalities and by their own investors, and the request flows downhill until it reaches a railing subcontractor being asked for an EPD. Most of the confusion in that conversation comes from a single misunderstanding: an environmental product declaration is not a certification and not a pass mark. It is a standardized disclosure document, and two of them can only be compared under fairly narrow conditions. Understanding what is actually in one, and where the carbon in an aluminum railing genuinely sits, lets a specifier make a decision that moves the number rather than one that just generates paperwork.
What an EPD is, and what it is not
An environmental product declaration is a Type III declaration prepared under ISO 14025, following a product category rule that dictates exactly how the underlying life-cycle assessment must be performed, and verified by an independent third party. It reports a set of impact indicators, of which global warming potential — expressed in kilograms of carbon dioxide equivalent — is the one everyone actually reads. Most construction product EPDs are cradle-to-gate, covering modules A1 through A3: raw material supply, transport to the factory, and manufacturing. Some extend to A4 and A5 for transport to site and installation, and a smaller number address end of life in modules C and D. Two EPDs are only comparable if they follow the same product category rule, cover the same modules, and use the same declared or functional unit — a declaration reported per kilogram of aluminum tells you something very different from one reported per linear metre of finished guard. Industry-average EPDs, such as those published for North American aluminum extrusions, are useful benchmarks but by definition do not reflect any specific supply chain.
Where the carbon in an aluminum railing actually sits
For an aluminum guard, the overwhelming majority of cradle-to-gate carbon is in the metal itself, and specifically in the electricity used to smelt it. Extrusion, cutting, machining, powder coating and assembly are real but comparatively small contributors. Transport from a Canadian plant to a Canadian site is usually a rounding error next to the billet. This has a blunt practical implication: a specifier who spends their effort optimizing packaging or shaving delivery distances while accepting billet of unknown origin is optimizing the wrong variable by an order of magnitude. The question that matters is where the aluminum was smelted and what powered the pot line.
The smelter is the entire story
Primary aluminum production is electro-intensive. Reported global average figures for primary aluminum sit in the region of sixteen kilograms of carbon dioxide equivalent per kilogram of metal on a full cradle-to-gate basis, heavily weighted by regions where smelters run on coal-fired electricity. Smelters powered by hydroelectricity produce a fraction of that — figures in the low single digits per kilogram are typical, and Canadian production is among the lowest-carbon primary aluminum in the world precisely because the great majority of it is smelted in Quebec on hydro power, with additional capacity in British Columbia. Canada is one of the world's larger primary aluminum producers, and for a project in Montreal, Ottawa, Toronto or Halifax, low-carbon metal is not an exotic import — it is the local product. Secondary, or recycled, aluminum is better still: remelting requires roughly five percent of the energy of primary production, which is why recycled content is such a powerful lever. All of these figures should be treated as approximate and confirmed against the specific EPD in front of you, because the numbers move with methodology and reporting year.
For an aluminum railing, almost every kilogram of carbon you can influence was decided at the smelter, before the extruder ever saw the billet.
Recycled content: useful, but read the fine print
Recycled content claims for extruded aluminum need care. Extrusion billet routinely contains a substantial proportion of recycled metal, but most of it is pre-consumer: the extruder's own process scrap, butt ends and offcuts, remelted in a closed loop. That is genuinely beneficial, and it is also not the same thing as post-consumer content, which is the metric most green building programs weight more heavily. The constraint on post-consumer scrap in architectural extrusion is metallurgical: alloys such as 6063 have tight compositional limits, and mixed post-consumer scrap carries contaminants that affect extrudability and, critically, surface quality after anodizing. A billet supplier can raise post-consumer content, but there is a real trade-off with finish quality on a product where a visible anodized or metallic finish is often the point. When you write a recycled content requirement, state whether you mean pre-consumer, post-consumer or total, and require the calculation method — otherwise you will receive three numbers from three suppliers that are not measuring the same thing.
Glass is not free either
On a glass guard, the aluminum framing may not be the largest carbon component. Float glass carries a lower carbon intensity per kilogram than primary aluminum — commonly reported in the range of one to one and a half kilograms of CO2 equivalent per kilogram — but glass is heavy. A laminated guard panel of two 6 mm plies weighs roughly 30 kg per square metre of glass alone, before hardware, and tempering and lamination add processing energy on top of the float production. Run the arithmetic and the glass in a frameless guard is a meaningful share of the assembly's footprint. This does not make glass the wrong choice; it makes glass thickness a carbon decision as well as a structural and cost decision, which is one more reason to size panels through engineering rather than by defaulting upward for comfort.
Writing a specification that actually lowers the number
- Ask for a facility-specific or manufacturer-specific EPD where one exists, and accept an industry-average EPD as a fallback rather than as an equivalent.
- Specify the smelting origin or a maximum GWP per kilogram for the billet. This single clause does more than every other sustainability requirement in a railing section combined.
- State recycled content as pre-consumer, post-consumer or total, and require the calculation method with the submittal.
- Confirm the declared unit before comparing numbers. Per kilogram, per square metre of guard and per linear metre are not interchangeable.
- Size glass through engineering rather than by defaulting to the next thickness up. Extra glass is extra carbon on every panel of the building.
- Weigh service life explicitly. A guard that lasts forty years without replacement halves its annualized impact against one replaced at twenty, which puts finish quality and corrosion detailing squarely inside the carbon conversation.
- Ask where fabrication happens. Domestic fabrication shortens the supply chain and, more importantly, gives you a traceable metal source to put in the submittal.
- Do not confuse an EPD with a performance threshold. Requiring a declaration proves disclosure; requiring a GWP limit is what changes what gets bought.
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Documentation, not guesswork
We fabricate in-house in Montreal and can trace and document what goes into your guards. If your project is reporting embodied carbon, bring us in at specification stage so the numbers are available when you need them.
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