Recycled construction materials: a purchase specification beats a circularity slogan
Recycled content is a property of a material, not a statement about whether it is suitable for a particular use. The specification is where that distinction is made or lost.

- Byline
- Gambit Reign analysis
- Period covered
- 2022–2024
- Reviewed
- 6 October 2026
- Topic
- Materials & packaging
- Reading time
- 6 min read
Key takeaways
- Specify recycled construction materials by intended use, performance class and evidence, exactly as a primary material is specified. A circularity claim is not a substitute for a specification and does not establish fitness for a particular application.
- Contaminants, testing regime, traceability and consistent supply are the practical questions that decide whether a recycled material can be used at scale, and each should be settled before the material is specified rather than after.
- Approvals and standards differ between the EU and GCC markets. The approach to specifying is transferable; the compliance position is not, and must be established per market and per project.
Recycled content is not a specification
There is a tendency in construction procurement to treat recycled content as a characteristic that makes a material preferable, and to stop there. Recycled content is a property of the material. It says something about its origin and nothing directly about whether it performs the function the project needs.
The consequence is that specifications are sometimes written around the recycled content rather than around the performance required, and the resulting material may not be suitable for the application it has been specified into. The failure is not the material's. It is the specification's, because a specification's job is to state what the material must do, and recycled content does not do that on its own.
The remedy is to specify a recycled material exactly as a primary material would be specified: by intended use, by the relevant performance class, and by the evidence that demonstrates conformance. The recycled content becomes a further requirement rather than the organising one.
The questions that decide whether it can be used
Beyond the performance class, several questions determine whether a recycled material can be used at scale on a project, and each is easier to answer before specification than after.
Intended use is the first and frames everything else. A material acceptable in a non-structural fill application may be unacceptable in a structural one, and a material acceptable in an external application may be unacceptable where it is exposed to a particular chemical environment. The application must be stated precisely, because 'recycled aggregate' covers an enormous range of materials of very different quality.
Contaminants are the second. Recycled streams carry the history of what they were before, and that history determines what is in them. The relevant contaminants depend on the source and on the application, and establishing acceptable limits is a specialist question that must be answered by qualified parties for the specific use.
Testing is the third, and it follows from the second. A specification should state what is tested, to what method, at what frequency, by whom, and against what acceptance criteria. A single certificate relating to a single sample does not establish the properties of a continuing supply.
Traceability is the fourth. Knowing where a material came from, and being able to demonstrate it, is what allows a deviation to be investigated and a claim to be substantiated. Traceability also underpins the circularity claim itself: a claim of recycled content that cannot be traced to a source is an assertion.
Consistent supply is the fifth, and it is the one most often discovered late. Recycled streams vary. A material that performed to specification in a trial may perform differently in a later delivery as the source stream changes. The specification should address how variation is managed, what the supplier must notify, and what happens when a delivery falls outside the acceptance criteria.
Transport distance belongs alongside these. A recycled material hauled a long distance to the site may carry a greater transport burden than a locally available primary material, which is why the comparison should be made on a consistent basis rather than assumed to favour the recycled option.
| Question | What the specification must state | Who must confirm |
|---|---|---|
| Intended use | The specific application and exposure conditions | Design team, against the project's own requirements |
| Performance class | The standard and class the material must meet for that use | Design team and specifier |
| Contaminants | Acceptable limits for the source history expected | Qualified specialist, per application |
| Testing | Method, frequency, sampling and acceptance criteria | Specifier, with testing by competent parties |
| Traceability | What records must accompany each delivery | Supplier, verified by the buyer |
| Supply consistency | Variation limits and the notification obligation | Supplier, with a contractual route for deviation |
| Risk allocation | Who carries the risk if the material fails to conform | Commercial and legal, agreed before award |
This question set is our own working framework. It states no contaminant limits, test methods or acceptance criteria, all of which are specialist and application-specific.
Risk allocation is part of the specification
Where a recycled material is specified, the question of who bears the risk if it does not conform is frequently left until it arises, at which point it is expensive to resolve.
The risk is real and it is different in character from the risk attaching to a primary material, because the variability of a recycled stream is inherently greater than that of a controlled primary product. That is not an argument against using recycled materials. It is an argument for allocating the risk deliberately in the contract, in the same way that any material with variable characteristics would be handled.
The allocation should address what evidence the supplier must provide, what happens if a delivery fails to meet the specified criteria, who bears the cost of the investigation and of any replacement, and how a disputed test result is resolved. Settling these in the specification and the contract, rather than when a problem emerges, is what makes using a recycled material a manageable decision rather than an open-ended one.
The 2024 protocol: retrospective context, not a 2022 requirement
The Commission published a Construction and Demolition Waste Protocol in 2024, which addresses how construction and demolition waste should be managed, including provisions relating to pre-demolition and pre-renovation audits. [D] It is a useful document and it is relevant to how recovered materials are generated and characterised.
It is important to place it correctly in time. This article covers a reference period beginning in 2022, and the 2024 protocol did not exist then. Where the article refers to it, it does so as retrospective context — an account of how thinking in this area developed — and not as a purported legal requirement applying during 2022. To present it otherwise would be to backdate a requirement, which would misrepresent the position at the time.
The distinction is not pedantic. A reader trying to understand what governed a project in 2022 needs to know what applied then, and a reader considering a project now needs to know what applies now. Blurring the two serves neither, and it is the kind of error that makes a retrospective unreliable.
What transfers and what does not
The analytical discipline set out above — specify by use, establish performance, control contaminants, test, trace, secure supply, allocate risk — transfers between markets without modification. It describes how to specify a material of variable provenance, which is a general problem.
The compliance position does not transfer. Standards, approval routes, testing requirements and the bodies responsible for them differ between the EU and the GCC, and they differ within the GCC between jurisdictions. A material accepted in one market is not thereby accepted in another, and an approval given by one authority has no standing with another.
That means a specification cannot be lifted from one market and applied in another without establishing the local position. The material questions are the same; the answers are jurisdiction-specific, and they should be confirmed for the project and the market rather than assumed from an analogous project elsewhere. The direction of travel in the region is toward more structured waste and materials regulation — Saudi Arabia's environment ministry, for instance, holds the mandate to regulate and supervise waste management and to encourage investment in the sector [E] — but a mandate of that kind establishes the framework, not the specific requirements a project must satisfy.
One further boundary deserves stating. Nothing here constitutes advice on the suitability of any specific material, and nothing here addresses hazardous materials, for which there are specific regulatory requirements and specialist obligations. Where a source stream may contain hazardous constituents, or where the application raises questions of that kind, the assessment must be made by qualified specialists under the applicable regime, and this article should not be read as offering guidance on it.
Limitations
- This article concerns how to specify recycled construction materials. It makes no statement that any material is or is not suitable for any application, and it contains no contaminant limits, test methods or acceptance criteria.
- It does not address hazardous materials, for which specific regulatory requirements and specialist assessment apply. Any question of that kind must be referred to qualified specialists under the applicable regime.
- The cited 2024 protocol is retrospective context for a reference period beginning in 2022 and does not represent a requirement in force during that period. No legal requirement should be inferred from its citation here.
- Approvals, standards and testing requirements differ between the EU and GCC markets and between jurisdictions. They must be confirmed for the specific project and market, and nothing here is compliance advice.
The next decision
Take one recycled material you intend to use and write its intended use and performance class before its recycled content — if you cannot, it is not yet specified.
Discuss your projectTaking this into your own project?
Our scoping guide and worksheet walk through the questions that make a brief usable — the decision, the evidence, the options including doing nothing, and what still has to be established. No email required.
Sources
External sources are referenced above by letter. Our own recommendations are identified as such in the text and are not attributed to these sources.
- [D]European Commission — Construction and Demolition Waste Protocol (2024)https://op.europa.eu/en/publication-detail/-/publication/d63d5a8f-64e8-11ef-a8ba-01aa75ed71a1/language-en
- [E]Saudi Ministry of Environment, Water and Agriculture — waste management mandate and circular economy contexthttps://mwared.mwan.gov.sa/en
