Factors · Formaldehyde (CH₂O) · Formaldehyde & aldehydes

How much formaldehyde is too much indoors?

A-0003 · Published 8 September 2026 · Updated 8 September 2026 · Coridum Research

  1. Sources Wood-based panels (particleboard, MDF, plywood)Laminate flooringBuilding materials
  2. Factors · start Formaldehyde (CH₂O)
  3. Outcomes Atopic dermatitis (eczema)Atopic dermatitis symptoms
  4. Interventions Source controlLow-emission materialsVentilation

Standards & bodies: World Health Organization (WHO)Methods: Exposure assessment

The World Health Organization guideline for indoor air is 0.1 mg/m³ of formaldehyde averaged over 30 minutes. In the measurements Coridum holds, a room with newly installed laminate flooring reached a mean of 0.038 ppm (F-0013), and a modelled residential room with 20 m² of medium density fibreboard at a ventilation rate of 0.5 h⁻¹ reached 0.093 mg/m³ (F-0015). The numbers that get quoted most often — class E1, E0.5, ENF — are none of these: they are limits for what a panel may emit in a test chamber.

Where it comes from indoors

Almost all of it comes from things made with resin. Wood-based panels — particleboard, medium density fibreboard, plywood — are bonded with formaldehyde-based adhesives, and the panel continues to release a small part of that for as long as it is in the room. Laminate flooring is a panel with a decorative surface, and behaves the same way. Furniture, kitchen carcasses, shelving and door blanks are all the same material under different names.

The consequence is that formaldehyde indoors is usually a question about surface area, not about a single object. One shelf changes nothing measurable; forty square metres of new fitted units in a closed flat is a different situation, and the same panel emitting the same amount per square metre produces a different concentration in each.

Exposure limits by jurisdiction

Two kinds of number are routinely confused here, and separating them is most of the answer to the question in the title.

What it applies to Body Value Averaging or test Source
The air in a room World Health Organization 0.1 mg/m³ 30 minutes WHO indoor air quality guidelines, 2010
A panel or article European Union, class E0.5 0.062 mg/m³ chamber, EN 717-1 F-0016
A panel European Union, class E1 0.124 mg/m³ chamber, EN 717-1 F-0018
A panel China, grade ENF 0.025 mg/m³ GB/T 39600-2021 F-0019
A panel United States, hardwood plywood 0.05 ppm large chamber, ASTM E 1333 F-0017

Only the first row is a value for the air you breathe. The rest are product limits, and a product that meets them can still produce a concentration above or below the guideline depending on how much of it there is and how the room is ventilated. The full set of ten product thresholds, with the test method for each, is in the formaldehyde emission limits table. Slovakia, the United Arab Emirates and Hong Kong are being compiled.

What it is linked to

The evidence Coridum holds on health effects is narrow and worth stating precisely rather than broadly. In a study of people with atopic dermatitis, those whose indoor formaldehyde fell by more than the group mean (a fall of 41.9 µg/m³) showed a greater reduction in their severity score than the rest: −2.69 against −1.48 (F-0026). The study did not state whether that difference was statistically significant, and it is a comparison within one group of people rather than a controlled trial.

That is the whole of what this article can say about health. The general case for keeping formaldehyde low rests on the World Health Organization guideline and the reasoning behind it, not on measurements held here.

What reduces it

Choosing the material. A panel certified to a stricter class emits less by definition, and that is source control at the point where it is cheapest — low-emission materials cost nothing extra to specify before an order is placed and cannot be retrofitted afterwards.

Ventilation is the second lever, and the modelled value above shows why it matters as much as the material: the 0.093 mg/m³ figure is not a property of the board, it is what 20 m² of that board produces at an air exchange rate of 0.5 h⁻¹ (F-0015). Double the exchange rate and the same board gives a lower number.

How strong is the evidence

Grade C for the source–factor link: newly installed laminate flooring and wood-based panels may be associated with raised indoor formaldehyde (C-0007), supported by consistent measurements in more than one study, with no contrary finding recorded.

Weaker than that for anything about health. The single relevant finding (F-0026) reports a difference in symptom score without stating significance, in people who already have a skin condition. It cannot carry a general statement about formaldehyde and health, and none is made here.

The product limits are a third kind of evidence again: they are what regulators decided, documented in one review (CKB 1163) and one study (CKB 0257), not measurements of any room.

What would settle it

A measurement in the room in question, over a period long enough to include the times when it is closed. The guideline is a 30-minute average, so a single reading taken with the window open answers nothing. What would settle the health question is a different kind of study altogether — one that changes the concentration deliberately and follows what happens — and the evidence layer behind this article does not contain one.

What the studies report

20 of 99 Findings — those cited in the text, then those with the strongest study design.

Linked toEffectPopulationStudy designSourceChecked
Atopic dermatitis (eczema) difference -2.69 per 41.9 children · home intervention study: environmentally friendly wallpaper and flooring in 24 homes F-0026 The effect of environmentally friendly wallpaper and floorin… (2014) machine
Laminate flooring mean 0.038 — · test room chamber and room measurement of two laminate flooring products F-0013 Pierce An assessment of formaldehyde emissions from laminate floori… (2016) machine
Wood-based panels (particleboard, MDF, plywood) mean 0.093 — · home chamber measurement combined with an indoor air model F-0015 Negrete-Carrillo et al. Formaldehyde Emissions from Wood Materials and Their Impact … (2026) machine
Wood-based panels (particleboard, MDF, plywood) limit 0.062 — narrative review of production, emissions and regulation F-0016 Gonçalves et al. Wood-Based Panels and Volatile Organic Compounds (VOCs): An … (2025) machine
Wood-based panels (particleboard, MDF, plywood) limit 0.05 — narrative review of production, emissions and regulation F-0017 Gonçalves et al. Wood-Based Panels and Volatile Organic Compounds (VOCs): An … (2025) machine
Wood-based panels (particleboard, MDF, plywood) limit 0.050 — narrative review of production, emissions and regulation F-0018 Gonçalves et al. Wood-Based Panels and Volatile Organic Compounds (VOCs): An … (2025) machine
Wood-based panels (particleboard, MDF, plywood) limit 0.025 — narrative review of production, emissions and regulation F-0019 Gonçalves et al. Wood-Based Panels and Volatile Organic Compounds (VOCs): An … (2025) machine
Atopic dermatitis symptoms difference 79.2 (19.6–168.4) per 10 % children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0278 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
Atopic dermatitis symptoms difference 39.9 (14.3–71.2) per 10 % children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0279 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
Atopic dermatitis symptoms difference 28.0 (6.6–53.7) per 10 % children aged 6 to 18 years with atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0280 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
Atopic dermatitis symptoms difference 17.8 (3.9–33.6) per 10 % children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0281 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
Atopic dermatitis symptoms difference 2.5 per 10 % children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0282 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
— mean 13.6 children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0283 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
— mean 18.1 children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0284 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
— mean 16.5 children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0285 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
— mean 12.5 children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0286 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
— mean 10.8 children with moderate-to-severe atopic dermatitis · home longitudinal (panel) study of children with moderate-to-severe atopic dermatitis in Seoul: real-time indoor formaldehyde monitoring at home and daily symptom scores (4,789 person-days), generalized linear mixed models adjusted for ambient PM2.5, temperature and relative humidity F-0287 Harmful Effect of Indoor Formaldehyde on Atopic Dermatitis i… (2021) machine
Birth outcomes beta -0.056 per 1 z-score pregnant women and their newborns · home birth cohort in Western Australia: formaldehyde, nitrogen dioxide and VOCs monitored in the homes of pregnant women at 34 weeks of gestation, associations with birth outcomes adjusted for maternal age, parity, asthma, diabetes, hypertension and season F-0331 Franklin et al. Maternal Exposure to Indoor Air Pollution and Birth Outcomes (2019) machine
Unvented heaters difference 9.4 (5.7–13.1) school children · classroom double-blind, cluster-randomised crossover trial in Australian school classrooms: low-NOx unflued gas heaters against non-indoor-emitting flued gas heaters, NO2 and formaldehyde measured with passive diffusion badges, children recorded symptoms, medication use and lung function twice daily F-0690 Respiratory Health Effects of Exposure to Low-NOx Unflued Ga… (2010) machine
Indoor plants (phytoremediation) the study says formaldehyde fell with passing time regardless of the plants, so the change cannot be read as an effect of the plants asthmatics and their households · home quasi-experimental study in the homes of asthmatics in Korea over two observation terms: households of continuation kept the indoor plants for both terms, households of withdrawal kept them for the first term and passed the second without any plants; formaldehyde and benzene, toluene, ethylbenzene and xylene were measured indoors, with peak expiratory flow rate twice a day and an asthma-specific quality of life questionnaire, compared with the Mann-Whitney test F-1220 House-plant placement for indoor air purification and health… (2014) machine

Each row is one Finding — a sentence as printed in one study, recorded with its page in the Coridum Knowledge Base. Follow the Finding number for the exact wording and the citation. Checked says who verified the row: machine means every automatic check passed and the surrounding text was read; person means someone read the sentence in the document. Rows are re-checked by a person over time. The studies are curated in the Coridum Knowledge Base; the reading of them together is a Claim, shown separately.

Claims this article rests on

A Claim is Coridum reading the Findings together, not a quotation from one study — according to Coridum. The grade follows the study designs behind it: A is the strongest, D means a single study or a mechanism.

Frequently asked questions

What is the guideline value for formaldehyde in indoor air?

The World Health Organization sets 0.1 mg/m³ averaged over 30 minutes as an indoor air quality guideline. It is a guideline for the air in a room, not a limit for a product.

Do the class E1 and E0 labels tell me what my room will contain?

No. Those are emission classes measured on a single panel in a standard chamber. What a room reaches depends on how much material is installed, how big the room is and how fast its air is exchanged.

How long does the rise after new flooring last?

The evidence here does not answer that directly. In one study, seven days after the flooring was removed again the concentration was back at the pre-installation background (F-0013) — which describes removal, not the natural decline of a floor that stays in place.

Sources

  1. Claim C-0007: Newly installed laminate flooring and wood-based panels may be associated with raised indoor formaldehyde.
  2. Finding F-0013: “Mean formaldehyde concentrations following installation were 0.038 and 0.022 ppm for Products 1 and 2 respectively, and 7 days after flooring removal the concentrations returned to background preinstallation levels.” (CKB 0257, p. 1)
  3. Finding F-0015: “For the typical residential ventilation scenario (0.5 h−1 ), concentrations decreased proportionally, reaching maximum values of 0.093 mg m−3 for MDF and 0.090 mg m−3 for melamine (20 m2 ).” (CKB 1036, p. 8)
  4. Finding F-0016: “In 2023, the European Commission established a new class E0.5 with a maximum emission limit for formaldehyde in wooden articles and furniture at 0.062 mg·m−3 air (half of the emission limit of class E1), which will be introduced in a revised version of EN 13986:2004+A1:2015 and will become compulsory from July 2026 [35].” (CKB 1163, p. 6)
  5. Finding F-0017: “After 2018, formaldehyde emissions in WBP produced and/or circulating in the USA must not exceed 0.05 ppm (0.061 mg·m−3 air) for hardwood plywood panels produced with a veneer or composite core, 0.11 ppm (0.135 mg·m−3 air) for MDF, 0.13 ppm (0.160 mg·m−3 air) for thin MDF and 0.09 ppm (0.111 mg·m−3 air) for PB [37].” (CKB 1163, p. 6)
  6. Finding F-0018: “The Chinese E1 corresponds to the European E1 (0.124 mg·m−3 air), while the Chinese E0 refers to panels with formaldehyde emissions higher than 0.025 mg·m−3 air but not exceeding 0.050 mg·m−3 air.” (CKB 1163, p. 7)
  7. Finding F-0019: “Grade ENF is used to classify panels with formaldehyde emissions equal to or lower than 0.025 mg·m−3 air [39].” (CKB 1163, p. 7)
  8. Finding F-0020: “CARB has established a formaldehyde emission standard of 0.11 ppm for MDF cores, as measured using a testing chamber.” (CKB 0257, p. 3)
  9. Finding F-0026: “However, subjects whose indoor FA concentration decreased greater than the mean (−41.9 μg/m3) showed a greater reduction of EASI score (−2.69 vs. −1.48).” (CKB 0606, p. 3)
  10. Data Table D-0004: Formaldehyde emission limits for wood-based panels (v1.0)
  11. Pierce An assessment of formaldehyde emissions from laminate flooring manufactured in China… (2016). Regulatory toxicology and pharmacology : RTP. doi:10.1016/j.yrtph.2016.06.022 CKB 0257
  12. Negrete-Carrillo et al. Formaldehyde Emissions from Wood Materials and Their Impact on Indoor Air Quality… (2026). doi:10.3390/su18147176 CKB 1036
  13. Gonçalves et al. Wood-Based Panels and Volatile Organic Compounds (VOCs): An Overview on Production, Emission Sources and Analysis (2025). Molecules. doi:10.3390/molecules30153195 CKB 1163
  14. The effect of environmentally friendly wallpaper and flooring material on indoor air… (2014). doi:10.5021/ad.2014.26.6.688 CKB 0606
  15. WHO guidelines for indoor air quality: selected pollutants. WHO Regional Office for Europe, 2010.

CKB = document number in the Coridum Knowledge Base, our curated library of peer-reviewed studies. Follow the DOI for the original paper.

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Coridum Research. How much formaldehyde is too much indoors? Coridum Knowledge A-0003, 8 September 2026. https://coridum.com/k/A-0003/

Stable reference: A-0003 — the citation carries the permanent link https://coridum.com/k/A-0003/, which never changes even if this page's address does. This page: https://coridum.com/knowledge/articles/how-much-formaldehyde-is-too-much-indoors/