Blog/VOCs and formaldehyde: ventilating to protect health
Contractors

April 2, 2026

6 min read

Updated August 7, 2026

Formaldehyde: the value that has applied since 2023, and what it changes on site

The French indoor-air value for formaldehyde changed on 1 January 2023, and not in the direction everyone expected: the 30 µg/m³ long-term figure disappeared, replaced by 100 µg/m³ over a short exposure. Plenty of trade literature still quotes the old value, or a 10 µg/m³ deadline that never came into force. Here is the current text, and the labelling thresholds you actually select products against.

Contents

The French indoor-air value for formaldehyde changed on 1 January 2023. The annex to article R221-29 of the environment code, rewritten by decree no. 2022-1689 of 27 December 2022, now sets 100 µg/m³ for short-term exposure, and no longer 30 µg/m³ for long-term exposure. The 10 µg/m³ deadline announced by the 2011 decree was replaced before it ever applied, which has not stopped trade literature from quoting it. On the product side the selection benchmark has not moved: the order of 19 April 2011 reserves class A+ for products whose formaldehyde stays below 10 µg/m³ after twenty-eight days of testing.

Understanding VOCs and formaldehyde on your job sites

What the term VOC covers (sources and pollutant families)

The term VOC covers organic compounds that evaporate at room temperature. The order of 19 April 2011 defines them precisely as compounds whose initial boiling point lies between 50 °C and 286 °C. On site, they are found in paints, varnishes, glues, sealants, solvents, foams, floor coverings and some cleaning products. Depending on the product you meet hydrocarbons, terpenes, glycol ethers and aldehydes. The common thread stays the same. They move from the material into the air, sometimes for several weeks after installation.

Formaldehyde: why it is watched especially closely indoors

Formaldehyde is an aldehyde very present in indoor air. It can be emitted by wood-based panels, glues, textiles, or during certain combustion processes. It is highly irritant and subject to close monitoring because it is linked to respiratory effects and a carcinogenic risk. In retrofits it deserves particular attention when replacing flooring, kitchens, cupboards and linings, which are precisely the packages where the exposed panel area is largest.

The values that count, and since when

Two reference frameworks coexist and do not do the same job. The first sets what is tolerated in the air of a room, the second what is tolerated at the emission of a product. Confusing them is the most common source of error on this subject.

Pollutant Value in force Exposure type Text
Formaldehyde 100 µg/m³ short term annex to article R221-29 of the environment code, since 1 January 2023
Benzene 2 µg/m³ long term same annex
Radon 300 Bq/m³ reference level same annex
Formaldehyde, Anses guideline 100 µg/m³ short term, to be met repeatedly and continuously through the day Anses update, 2018
Formaldehyde, former value 30 µg/m³ long term decree no. 2011-1727, superseded on 1 January 2023

The second framework is the health emissions label. Concentrations are measured after twenty-eight days in an emission test chamber, in a conventional 30 m³ reference room ventilated at 0.5 air changes per hour. That 0.5 ach is a test convention, not a ventilation recommendation for your jobs, and it is frequently quoted as though it were one.

Substance, exposure concentration in µg/m³ A+ A B C
Formaldehyde < 10 < 60 < 120 > 120
Total VOCs < 1,000 < 1,500 < 2,000 > 2,000
Acetaldehyde < 200 < 300 < 400 > 400
Toluene < 300 < 450 < 600 > 600
Styrene < 250 < 350 < 500 > 500
1,4-dichlorobenzene < 60 < 90 < 120 > 120

The letter shown on the label is the worst class obtained across all substances, total VOCs included. A product can therefore be rated C because of a single line, and it is the technical data sheet, not the label, that tells you which one. On a quotation the consequence is simple: "A+ rated products" commits to nothing if the work package is not named. Write the required class package by package, boards and floor substrates, adhesives and primers, paints and varnishes, sealants and joints, because those are the four families that weigh most on the formaldehyde load of a freshly refurbished room, and because it is the only wording that lets you refuse a substitution mid-job.

Identifying the main sources of VOCs after a renovation

Paints, glues, varnishes, panels: the materials that off-gas the most

Right after the work, the biggest VOC emitters are wet products (paints, varnishes, glues, sealants) and some wood panels (chipboard, MDF, OSB) that release solvents and formaldehyde. Aim for low-emission products, let them dry through according to the data sheet, and leave ventilation running continuously for the first few days. Developed area matters as much as the product: a lining package shifts the order of magnitude of a job far more than a tin of paint.

Furniture, textiles, cleaning products: the off-site contributions not to forget

A home handed over new then reloads with furniture and textiles. Mattresses, sofas, curtains, rugs, scented sprays and household products bring VOCs you did not install. The point of documenting that is not to lecture the occupant, it is to bound what belongs to your package before a late measurement is held against you.

Airtightness and humidity: when energy performance traps pollutants

As insulation and airtightness improve, concentration rises unless ventilation is brought up to standard in the same job. Drying renders, leaks and showers add a moisture load that encourages odours and emissions. Check the ventilation flow rates against the values in the order of 24 March 1982 and record the readings. To go further, rely on ventilation flow rate measurement to concretely verify that the air is properly renewed.

Ventilating effectively to reduce VOCs and protect air quality

Site ventilation: what you control during and after the work

During application and drying, ventilation is a site resource, not an instruction to hand to the occupant. Keep the ventilation running continuously, open up across the plan during application, and avoid raising the temperature sharply to speed up drying: you push emissions rather than clearing them. The tipping point is recommissioning, when control passes from you to the installation, and when the settings have to be made and recorded.

Single-flow, humidity-controlled, heat-recovery ventilation: choosing by home and budget

Once site ventilation stops, only the permanent installation sustains air renewal. Self-regulating single-flow is the most accessible. Humidity-controlled systems modulate flow with humidity, provided the system holds a technical approval. Heat-recovery ventilation reclaims warmth, but demands ductwork, filters and space. In a retrofit the decision follows fabric airtightness, available loft space and duct accessibility. To go further on installing heat-recovery ventilation, its constraints and its benefits, see our dedicated guide.

Settings, balancing, air inlets: the control points that make the difference

Ventilation performs when it is set and recorded. Check that the air inlets are unobstructed, that extract points are correctly placed, that ducts do not leak and that the network is clean. On a heat-recovery unit, check filters and flow balancing. A missed adjustment lets pollutants stagnate and cancels the health gain of your product selection, which makes the premium for A+ references impossible to defend on the quote.

Measuring and proving the improvement in air quality in 2026

When to run VOC and formaldehyde measurements (before/after work, handover)

To get objective evidence of the work's effect, start with a baseline before the job. Run another campaign after commissioning and setting the ventilation, then at handover, once the materials are dry. On fresh paint, glue or flooring, an early measurement overstates emissions and turns against you: it documents a drying peak you will then have to explain.

Consumer sensors vs laboratory measurements: what is actually defensible

Consumer sensors (CO2, humidity, particulates, TVOC) are for steering and for spotting a drift. CO2 is in fact the only one of those parameters whose measurement is framed by a text, and only for premises open to the public, a subject covered in our article on CO2 sensor control. To prove a reduction in VOCs or formaldehyde, only an accredited laboratory working to a standardised protocol produces a defensible result.

Tracking your actions: ventilation record, photos, manuals and emission classes

Keep a ventilation record with measured flow rates, extract point positions, filter change dates, and before and after photographs. Add the technical data sheets and emission classes of the products used, the air inlet references, and the usage instructions handed over. That file is what turns a technical choice into evidence, and it is the only thing still standing twelve months later.

Best practice to limit VOC emissions from the product choice onward

Product selection: labelling, technical data sheets, indoor emissions

When buying, aim for the A+ indoor air emissions label wherever possible, knowing it corresponds to under 10 µg/m³ of formaldehyde and under 1,000 µg/m³ of total VOCs in the test conditions. Cross-check against the technical data sheet and the safety data sheet. Look for water-based or low-odour wording, and rule out solvent-heavy products where an alternative exists. For glues and sealants, insist on an emission class, not just a VOC content on the packaging.

Site organisation: storage, drying times, temperature rise, air purging

Store tins closed, away from heat, and open them at the last moment. Respect the drying times stated by the manufacturer. If you heat the space, raise the temperature gradually so you do not push the off-gassing. During and after application, keep the ventilation running and purge the air with short, effective airing, especially in small volumes where concentration climbs fastest.

Defending the premium on A+ products against a cheaper bid

The premium on an A+ range is defended with a figure, not with a general health argument. Class C allows over 120 µg/m³ of formaldehyde as an exposure concentration, class A+ under 10: a factor of twelve on the same test method, at identical installed area. Put the emission class in plain text on every affected quote line. That is what makes your offer comparable item by item, and it is also what protects you if a measurement is requested afterwards. On the quote, that information belongs line by line, alongside the technical characteristics each measure has to carry.

Key figures

100 µg/m³

Indoor air value for formaldehyde, short-term exposure

2 µg/m³

Indoor air value for benzene, long-term exposure

< 10 µg/m³

Formaldehyde required for the A+ emission class

Frequently asked questions

The French order of 19 April 2011 quantifies emission classes A+ to C substance by substance, as an exposure concentration measured after twenty-eight days in an emission test chamber. For class A+, formaldehyde must stay below 10 µg/m³ and total VOCs below 1,000 µg/m³. So insist on the A+ label for paints, glues, varnishes, coverings and panels, and ask for the technical data sheet rather than trusting a VOC content printed on the tin, which does not answer to the same test method.

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Pierre-Louis Guhur

Pierre-Louis is CEO and co-founder of Argile. He holds a PhD in machine learning, written at Inria, and renovated a house with his own hands in 2017 before founding the company. On the blog he writes about what he implements in the software: the 3CL-DPE 2021 method, NF EN 12831 and building physics as a calculation engine has to handle them, assumption by assumption.

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Installing an air-to-water heat pump

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