
The Specification Problem Nobody Talks About
Ask any experienced architect what they specify for acoustic treatment in a commercial interior, and you will likely hear one of a handful of answers: mineral wool, acoustic foam, or, increasingly, a felt panel made from recycled PET. Ask them why, and the answers become less confident. ‘It’s what we’ve always used.’ ‘The client wanted something natural.’ ‘The supplier said it was sustainable.’ In a field where specification decisions shape buildings for decades, these are somewhat uncomfortable answers.
The acoustic materials market is undergoing a genuine transition. Sustainability has moved from a checkbox to a structural specification requirement, driven by BREEAM, WELL, LEED, along with an accelerating adoption of net-zero targets across commercial real estate, and yet, despite this shift, many of the assumptions that govern material selection were formed in a ‘pre-sustainability’ era and have never been rigorously tested against the evidence now available.
This piece addresses that gap directly. Drawing on published Environmental Product Declarations (EPDs), third-party certified recycled content data, and lifecycle analysis from across the acoustic materials sector, we examine the evidence behind three of the most persistent misconceptions shaping specification decisions today.

Misconception 1: ‘Natural Materials Are Inherently More Sustainable’
This is perhaps the most pervasive and consequential misconception in the market. The logic feels intuitively sound: sheep’s wool is biodegradable, renewable, and agricultural. Recycled PET felt is made from plastic bottles. Plastic, in the popular imagination, is bad. Natural, by definition, is good.
The data tells a more complicated story. Sheep’s wool acoustic panels contain, by definition, zero post-consumer recycled (PCR) content. The fibre is virgin, however renewable the source, it has not been diverted from a waste stream. Recycled PET felt, by contrast, is composed of up to 60–85% post-consumer recycled content, depending on manufacturer, sourced directly from collected plastic bottles that would otherwise enter landfill or the ocean. On the single metric of material waste diversion, the act of rescuing an existing resource rather than extracting a new one, PET felt has no comparison in the acoustic panel category.
Fundamentally, we have to avoid dealing in absolutes. Biodegradable does not mean low-impact. Renewable does not mean zero-carbon. The data behind each claim matters more than the category it falls into.
The lifecycle picture is equally instructive. Sheep farming carries a substantial carbon footprint driven by methane emissions from livestock, a greenhouse gas with significantly higher short-term global warming potential than CO₂, which contributes to the carbon profile of sheep farming. Wool also requires washing (scouring), often with significant water and chemical inputs, before it can be processed into usable acoustic fibre. Supply chains are typically long and geographically complex. Third-party EPDs for finished wool acoustic panels, the mechanism by which lifecycle carbon can be independently verified, are rarely published, making like-for-like comparison with PET felt products difficult. Where EPDs do exist for PET felt products, they support a compelling embodied carbon story: the thermal bonding process that creates PET felt requires no chemical binders, generates no toxic by-products, and produces panels that are 100% recyclable at end of life.
“Biodegradable does not mean low-impact. Renewable does not mean zero-carbon. The data behind each claim matters more than the category it falls into.”
This is not an argument that wool is a poor material choice. Without question, it has legitimate acoustic properties, genuine thermal benefits, and a biodegradability advantage that matters in specific contexts. But the claim that wool is ‘more sustainable’ than PET felt, stated as a categorical truth, is not supported by the available evidence. It is, at best, a context-dependent assertion that depends heavily on which sustainability metric you prioritise, and at worst, a shorthand assumption that has substituted for proper analysis.
Understanding Renewable vs. Recycled
Renewable materials (wool, timber, cork) replenish naturally and are often biodegradable. Recycled materials (PET felt, recycled glass, reclaimed steel) divert existing resources from waste. Both matter, but they address different sustainability challenges. Renewable materials reduce extraction pressure; recycled materials close material loops. For BREEAM Mat 01 and LEED MR credits, post-consumer recycled content (PCR) is the metric most directly rewarded, not renewability. Specifiers should understand which metric a material claim is addressing before accepting it at face value.

Misconception 2: ‘Eco-Branded Materials Are Equally Sustainable’
The proliferation of sustainability language in the acoustic and interior fit-out market has created a new problem: greenwash camouflage. When every product carries the language of environmental responsibility, ‘eco’, ‘natural’, ‘sustainable’, ‘responsible’, ‘circular’, the signal becomes noise. For the specifier trying to make a genuine sustainability case to a client, or to evidence a BREEAM credit, the vocabulary of sustainability is no longer enough.
Consider three material types that are frequently positioned as sustainable alternatives to conventional acoustic treatment, and examine what the evidence actually supports.
Acoustic Foam
Standard acoustic foam, polyurethane or melamine, is petroleum-derived, typically contains no post-consumer recycled content, and presents severe end-of-life challenges. Polyurethane foam is non-biodegradable, largely unrecyclable in practice, and its dominant disposal route in the UK is landfill or, at best, incineration. Environmental Product Declarations are rarely published for specification-grade foam products. Despite this, foam continues to be specified under the broad umbrella of ‘acoustic treatment’ without the scrutiny applied to other categories. Some manufacturers have introduced recycled foam variants using post-industrial scrap (PIR content), but post-consumer content remains negligible across the mainstream market. As such, foam’s recycled content and end-of-life limitations are increasingly scrutinised in sustainability-led specifications.
Mineral Wool
Mineral wool, rockwool or stonewool, is one of the most widely specified acoustic and insulation materials in commercial construction, and its sustainability credentials are frequently overstated. The primary raw material is virgin igneous rock, melted at approximately 1,500°C, thereby requiring huge energy input. Further, post-consumer recycled content is effectively zero. Some mineral wool formulations incorporate pre-consumer industrial slag as a secondary raw material, contributing to total recycled content of perhaps 20–30%, but PCR, the metric that counts toward green building certification credits, is often negligible.
Mineral wool is also, in practical terms, effectively non-recyclable. Mineral wool fibres cannot be easily separated from construction substrate at end of life, and contaminated off-cuts are typically landfilled. The fibres cause skin and respiratory irritation during handling, a key material health consideration that is absent from most comparative sustainability discussions. Mineral wool does carry an important advantage in fire performance, and its thermal and acoustic credentials are well-established. However, its environmental profile, specifically its recycled content story is weak, and the assumption that it represents a ‘safe’ sustainable default deserves interrogation.
Glass Wool
Glass wool presents the most nuanced case. It does incorporate a genuine proportion of recycled glass, typically around 40–70% total recycled content, making it amongst the strongest performers among the traditional materials on this metric. However, a meaningful distinction is often overlooked in supplier marketing: much of this recycled glass is pre-consumer cullet (manufacturing off-cuts), not post-consumer recycled material. Where PCR content is independently verified, and public disclosures are limited, it typically represents approximately 20–27% of the finished product, significantly lower than PET felt. Glass wool also contains organic resin binders that complicate recyclability and can affect indoor air quality where VOC performance is a specification criterion.
Note: PCR vs. Total Recycled Content
Post-Consumer Recycled (PCR) content refers to material recovered after consumer use e.g. plastic bottles, glass containers and worn textiles. Post-Industrial Recycled (PIR) content refers to manufacturing off-cuts and factory waste that never reached a consumer. Both contribute to ‘total recycled content’, but PCR is considered the more rigorous claim and carries greater weight in BREEAM, LEED, and WELL assessments. A product claiming 70% recycled content may contain very little PCR. Always interrogate the split.

Misconception 3: ‘Novel and Emerging Materials Have Better Sustainability Credentials’
Beyond the established categories, a newer cohort of acoustic and interior materials has entered the specification conversation across all manner of emerging formats, from hemp-based panels to mycelium composites and cork-faced acoustic boards, as well as various agricultural waste-derived products. These materials are frequently presented at trade events and in design media as the frontier of sustainable specification, and they attract considerable attention precisely because they are novel.
Some of these materials will, in time, develop robust sustainability evidence bases. Mycelium composites in particular show promise as a truly circular, biodegradable material grown from agricultural waste. Hemp-based boards offer a genuinely low-embodied-carbon fibre with good acoustic properties. But the specifier should approach this category with particular care, because it is precisely the category in which the gap between aspiration and evidence is widest.
Very few novel acoustic materials carry independently verified EPDs. Acoustic performance data, particularly for the frequency ranges relevant to commercial office environments, is often limited to laboratory samples rather than installed system performance. Supply chains are frequently short-run and geographically concentrated, with implications for cost, lead time, and consistency at scale. Further, the durability and maintenance requirements of biological and agricultural-derived materials in commercial interiors, where cleaning protocols, humidity cycling, and physical wear are demanding, are not yet well-characterised.
Innovation is welcome, but it should be tested and not taken on trust. The sustainability conversation should always be governed by evidence, especially when the evidence is new. The question for the specifier is not whether these materials are interesting, they are, but whether the sustainability claims attached to them can withstand the same evidential scrutiny we should be applying to all material choices. At present, for most novel acoustic materials, the honest answer is: not yet. PET felt, by contrast, has a decade of commercial installation data, independently verified recycled content figures, published EPDs from leading manufacturers, and a well-characterised end-of-life recycling pathway through the PET stream, the most widely recycled plastic globally.
“Innovation is welcome, but it should be tested and not taken on trust. The sustainability conversation should always be governed by evidence, especially when the evidence is new.”

What Does Good Specification Practice Look Like?
The purpose of this analysis is not to position any single material as the universal answer. Acoustic specification is rightly context-dependent, where acoustic target, aesthetic, sustainability and, above all, budget will all shape the right choice for any given project. Rather the purpose is to establish that the evidence required to make a genuinely sustainable material choice exists, and that the specification profession has both the access and the responsibility to use it.
Concretely, good practice looks like this:
In Conclusion: The Case for PET
PET felt is not a new material, and it does not require advocacy. What it requires is honest comparison, the kind that the broader market has been slow to apply. Viewed against the wider evidence available, if we take recycled content performance as an example metric, specification-grade recycled PET felt clearly performs strongly relative to traditional acoustic material categories. Similarly, on verification transparency, it benefits from widely available EPDs and PCR certification. On circularity, its compatibility with established PET recycling systems provides a credible pathway, even if infrastructure challenges remain.
It also, on the available evidence, outperforms most of the ‘natural’ and novel alternatives currently being positioned as its sustainability superiors. This is not because PET felt is perfect, the end-of-life recyclability of installed panels through mainstream UK waste infrastructure remains a genuine industry challenge, shared across the category, but because the honest application of the same evidential standard to all materials in the category produces this result.
The market for acoustic materials is maturing rapidly. Specifiers, sustainability practitioners, and end clients are asking harder questions, and the gap between assertion and evidence is narrowing. The materials that will define the coming years of commercial interior specification are not necessarily the newest or the ones with the most evocative brand narratives, they are the ones that can answer hard questions with clear data.
The question worth asking, of every material on your next schedule of finishes, is simple: show me the evidence. It is a question the acoustic materials market, as a whole, is only just beginning to take seriously.

References
Evidence-based specification protects not only the environment, but professional credibility. In an increasingly regulated claims landscape, data is not optional. It is essential.
This article draws upon publicly available, independently verified sustainability data across the acoustic materials sector. Comparative analysis is based on a range of authoritative sources, including:
Where recycled content percentages are referenced, these are derived from publicly disclosed documentation and, where available, independently verified certification statements.
Lifecycle commentary is based on published EPD datasets and peer-reviewed academic sources.
Data reflects information available at the time of writing (February 2026). As disclosure practices and formulations vary by manufacturer and product line, specifiers are encouraged to review product-specific documentation for each project.
This article is intended to support informed specification discussion and does not constitute product-level certification or lifecycle verification.
About the Author
This piece has been written by James Bell of Dragonfly Sustainability Ltd., an independent sustainability consultancy specialising in lifecycle analysis, material performance benchmarking, carbon reporting and environmental compliance within the furniture and interior fit-out sector.
With over a decade of experience across manufacturing, supply chain and ESG strategy, James supports brands and specifiers in translating sustainability claims into evidence-based, defensible communication aligned with green building frameworks and regulatory guidance.
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