Factors · Carbon dioxide (CO₂) · Schools & education
How much CO₂ is too much in a classroom?
- Sources Continuous and constant sources
- Factors · start Carbon dioxide (CO₂)Relative humidity
- Interventions VentilationAir exchange rate (air changes per hour)
Standards & bodies: ASHRAEWorld Health Organization (WHO)Methods: Non-dispersive infrared (NDIR) methodLow-cost sensors
Standards put the line for classrooms at 1000 ppm to 1500 ppm as a daily average. Measurement campaigns find that real classrooms spend most of the school day above it: in one school the recommended 1000 ppm limit was exceeded 89.3 % of the time (F-0038), and across the European SINPHONIE campaigns schoolchildren were exposed to a mean of 1433 ppm, with individual measurements reaching 4957 ppm (F-0039).
Where the carbon dioxide in a classroom comes from
It comes from the pupils. Carbon dioxide indoors is a continuous and constant source in the technical sense: people exhale it steadily for as long as they are in the room, so the concentration is set by how many people are in the room and how fast the air is exchanged, not by any material or product.
That is why the number is used as a proxy rather than as a hazard. At the concentrations reached in classrooms carbon dioxide is not itself the thing to worry about; it is the visible part of a problem that also carries everything else people and rooms release — odours, volatile compounds, and the respiratory aerosols by which infections spread. Ventilation removes them together, and carbon dioxide is the only one of them that a school can afford to measure continuously.
Exposure limits by jurisdiction
None of these is a toxicity limit. They are ventilation targets: the value at which the body issuing them considers the air exchange adequate.
| Body | Threshold | Applies to | Source |
|---|---|---|---|
| UK Department for Education, BB101 (2018) | 1000 ppm daily average (mechanical ventilation); 1500 ppm daily average (natural ventilation); not above 2000 ppm for more than 20 consecutive minutes | classrooms during occupied hours | BB101 |
| German Environment Agency, UBA (2008) | below 1000 ppm hygienically harmless; 1000–2000 ppm elevated, ventilate; above 2000 ppm unacceptable | all indoor spaces | UBA |
| ANSI/ASHRAE Standard 62.1 | about 700 ppm above the outdoor concentration at the standard’s ventilation rate | design reference | ASHRAE 62.1 |
Slovakia, the United Arab Emirates and Hong Kong are being compiled; the comparison across jurisdictions is kept in the indoor air quality limits table.
What classrooms actually measure
Three independent campaigns give the picture.
| What was measured | Value | Where | Finding |
|---|---|---|---|
| Share of school-day time above the recommended 1000 ppm | 89.3 % | one school | F-0038 |
| Mean exposure of schoolchildren, range 269–4957 ppm | 1433 ppm | SINPHONIE, European campaigns | F-0039 |
| Average school-day concentration (standard deviation 405 ppm) | 841 ppm | monitored classrooms | F-0041 |
| 99.9th percentile of daily maxima | 5080 ppm | the same classrooms | F-0042 |
The two averages look contradictory and are not. A mean of 841 ppm across whole school days (F-0041) sits alongside daily peaks past 5000 ppm (F-0042) in the same set of classrooms: the average is pulled down by empty rooms, breaks and open windows, while the peak is what a full room reaches before anyone opens one. This is why a single spot measurement says very little, and why the standards are written as daily averages plus a short-term ceiling.
What lowers it
Mechanical ventilation. Two of the campaigns compared classrooms that had it with classrooms that did not, and both found lower concentrations where it was present: in SINPHONIE a mean of 1087 ppm against 1510 ppm (F-0040), and in the second campaign lower concentrations and less variability in schools with central mechanical ventilation (F-0043). Taken together these support a claim of moderate strength: in classrooms, mechanical ventilation may lower indoor carbon dioxide (C-0018).
Where mechanical ventilation does not exist, the lever is the air exchange rate achieved by opening windows — and the evidence we hold does not tell us how much any particular window-opening routine achieves. That is a gap, not a recommendation.
How strong is the evidence
Grade C. All four studies behind the numbers above are measurement campaigns rather than experiments: they measure what classrooms are like, and where mechanical ventilation is present they measure it alongside everything else that tends to come with a newer, better-equipped building. The direction is consistent across two independent campaigns in different countries, which is why the claim is graded C and not D — but consistency between observational campaigns is not the same as a controlled comparison, and no study here randomised anything.
The limits in the table come from a different kind of document again: guidance and standards, not measurements. They tell you what a body decided was acceptable, not what happens at that value.
What this article does not show is any effect on pupils. The evidence layer behind it contains no finding linking classroom carbon dioxide to attention, test results or absence — so no such sentence appears here, however often it is repeated elsewhere.
What would settle it
Two things. First, a controlled comparison: the same classrooms, the same pupils, ventilation changed deliberately, with the outcome measured — not a survey of schools that already differ in a dozen ways. Second, our own measurements. A logged school day in a specific classroom, against the thresholds in the table above, answers the question that a parent or a head teacher actually has, which is not “what do classrooms look like on average” but “what does this room do at 11 a.m. in February”.
What the studies report
20 of 175 Findings — those cited in the text, then those with the strongest study design.
| Linked to | Effect | Population | Study design | Source | Checked |
|---|---|---|---|---|---|
| — | share-above 89.3 | students · classroom | measurement campaign in two newly renovated schools during the heating season, with attention testing | F-0038 Klavina Carbon dioxide as indoor air quality indicator in renovated … (2016) | machine |
| — | mean 1433 | schoolchildren · classroom | European school measurement campaign (SINPHONIE final report) | F-0039 SINPHONIE Schools Indoor Pollution and Health Observatory Ne… (2014) | machine |
| HVAC systems | mean 1087 | schoolchildren · classroom | European school measurement campaign (SINPHONIE final report) | F-0040 SINPHONIE Schools Indoor Pollution and Health Observatory Ne… (2014) | machine |
| — | mean 841 | students · classroom | continuous monitoring of Boston public school classrooms over a school year, 245 million measurements | F-0041 Ge Decision tools for schools using continuous indoor air quali… (2025) | machine |
| — | other 5080 | students · classroom | continuous monitoring of Boston public school classrooms over a school year, 245 million measurements | F-0042 Ge Decision tools for schools using continuous indoor air quali… (2025) | machine |
| HVAC systems | — | students · classroom | continuous monitoring of Boston public school classrooms over a school year, 245 million measurements | F-0043 Ge Decision tools for schools using continuous indoor air quali… (2025) | machine |
| Mechanical ventilation | difference 491 | — · classroom | ventilation intervention study in classrooms: mechanical ventilation set to a carbon dioxide threshold in twelve classrooms and the measured concentrations compared with the baseline week | F-1651 A ventilation intervention study in classrooms to improve in… (2013) | machine |
| Mechanical ventilation | mean 841 | — · classroom | ventilation intervention study in classrooms: mechanical ventilation set to a carbon dioxide threshold in twelve classrooms and the measured concentrations compared with the baseline week | F-1652 A ventilation intervention study in classrooms to improve in… (2013) | machine |
| Cognitive performance | difference -13.57 | college students · test chamber | controlled chamber exposure experiment with college students in Chongqing: 4-hour exposures to 500 ppm and 2500 ppm pure CO2 with and without added negative air ions, cognitive test battery and symptom questionnaires | F-0399 Effects of increasing indoor negative air ions on cognitive … (2023) | machine |
| Cognitive performance | difference 11 | adult volunteers · exposure chamber (office-like) | blinded controlled exposure study with balanced crossover order: 22 participants in six groups exposed in an office-like chamber to CO2 at 600, 1,000 and 2,500 ppm in three 2.5-hour sessions on one day, ventilation rate and temperature constant, computer-based Strategic Management Simulation test of decision-making performance analysed with analysis of variance | F-0416 Is CO2 an Indoor Pollutant? Direct Effects of Low-to-Moderat… (2012) | machine |
| Cognitive performance | difference 23 | adult volunteers · exposure chamber (office-like) | blinded controlled exposure study with balanced crossover order: 22 participants in six groups exposed in an office-like chamber to CO2 at 600, 1,000 and 2,500 ppm in three 2.5-hour sessions on one day, ventilation rate and temperature constant, computer-based Strategic Management Simulation test of decision-making performance analysed with analysis of variance | F-0417 Is CO2 an Indoor Pollutant? Direct Effects of Low-to-Moderat… (2012) | machine |
| Cognitive performance | difference 44 | adult volunteers · exposure chamber (office-like) | blinded controlled exposure study with balanced crossover order: 22 participants in six groups exposed in an office-like chamber to CO2 at 600, 1,000 and 2,500 ppm in three 2.5-hour sessions on one day, ventilation rate and temperature constant, computer-based Strategic Management Simulation test of decision-making performance analysed with analysis of variance | F-0418 Is CO2 an Indoor Pollutant? Direct Effects of Low-to-Moderat… (2012) | machine |
| Cognitive performance | difference 94 | adult volunteers · exposure chamber (office-like) | blinded controlled exposure study with balanced crossover order: 22 participants in six groups exposed in an office-like chamber to CO2 at 600, 1,000 and 2,500 ppm in three 2.5-hour sessions on one day, ventilation rate and temperature constant, computer-based Strategic Management Simulation test of decision-making performance analysed with analysis of variance | F-0419 Is CO2 an Indoor Pollutant? Direct Effects of Low-to-Moderat… (2012) | machine |
| Cognitive performance | decision-making performance filed under cognitive-performance | adult volunteers · exposure chamber (office-like) | blinded controlled exposure study with balanced crossover order: 22 participants in six groups exposed in an office-like chamber to CO2 at 600, 1,000 and 2,500 ppm in three 2.5-hour sessions on one day, ventilation rate and temperature constant, computer-based Strategic Management Simulation test of decision-making performance analysed with analysis of variance | F-0420 Is CO2 an Indoor Pollutant? Direct Effects of Low-to-Moderat… (2012) | machine |
| Cognitive performance | decision-making performance filed under cognitive-performance; the focused activity scale moved in the opposite direction | adult volunteers · exposure chamber (office-like) | blinded controlled exposure study with balanced crossover order: 22 participants in six groups exposed in an office-like chamber to CO2 at 600, 1,000 and 2,500 ppm in three 2.5-hour sessions on one day, ventilation rate and temperature constant, computer-based Strategic Management Simulation test of decision-making performance analysed with analysis of variance | F-0421 Is CO2 an Indoor Pollutant? Direct Effects of Low-to-Moderat… (2012) | machine |
| Ventilation | maximum level recorded as measure other; the value after is printed as a range and sits in extra | university students and staff (outbreak contacts) · university classroom | outbreak investigation with a contact cohort: 27 tuberculosis cases and 1665 contacts in underventilated university buildings in Taiwan, indoor CO2 measured before and after ventilation engineering, incidence of TB among contacts analysed with adjustment for contact investigation and latent TB infection treatment | F-0443 Effect of ventilation improvement during a tuberculosis outb… (2020) | machine |
| Tuberculosis | other 97 (50–99.9) | university students and staff (outbreak contacts) · university classroom | outbreak investigation with a contact cohort: 27 tuberculosis cases and 1665 contacts in underventilated university buildings in Taiwan, indoor CO2 measured before and after ventilation engineering, incidence of TB among contacts analysed with adjustment for contact investigation and latent TB infection treatment | F-0444 Effect of ventilation improvement during a tuberculosis outb… (2020) | machine |
| Tuberculosis | — | university students and staff (outbreak contacts) · university classroom | outbreak investigation with a contact cohort: 27 tuberculosis cases and 1665 contacts in underventilated university buildings in Taiwan, indoor CO2 measured before and after ventilation engineering, incidence of TB among contacts analysed with adjustment for contact investigation and latent TB infection treatment | F-0445 Effect of ventilation improvement during a tuberculosis outb… (2020) | machine |
| Cognitive performance | primary outcome null result of a crossover trial; the Results sentence 'There were no significant exposure effects on cognitive performance' is split across a line break in the text layer | schoolchildren aged 10-12 years · climate chamber (sleeping) | double-blind, placebo-controlled, fully balanced crossover trial: 36 children aged 10-12 years slept in a climate chamber in 6 groups under three conditions seven days apart in random order (high ventilation with CO2 at 700 ppm; high ventilation with added pure CO2 at 2000-3000 ppm; reduced ventilation with CO2 at 2-3000 ppm and bioeffluents), CANTAB cognitive test battery in the evening and next morning, sleep monitored with wrist actigraphs | F-0449 The effect of air quality on sleep and cognitive performance… (2023) | machine |
| — | median 110 | geriatric inpatients and staff · hospital patient room | randomized, sham-controlled, crossover, open-label trial (February to May 2021): CO2 monitors placed in twelve double-bed patient rooms across two geriatric wards of a Belgian hospital, staff instructed to open windows, increase air exchange and reduce crowding to keep CO2 at or below 800 ppm; primary outcome time per day above 800 ppm | F-0474 Laurent Monitors to improve indoor air carbon dioxide concentrations… (2022) | 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
-
In classrooms, mechanical ventilation may lower indoor carbon dioxide: two independent measurement campaigns found lower concentrations where central mechanical ventilation was present than where it was not.
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 carbon dioxide level should a classroom stay under?
The UK schools standard sets 1000 ppm as a daily average where ventilation is mechanical and 1500 ppm where it is natural, and says the concentration should not exceed 2000 ppm for more than 20 consecutive minutes. The German assessment treats anything under 1000 ppm as hygienically harmless and anything above 2000 ppm as unacceptable.
Do real classrooms stay under those numbers?
Often not. One school campaign found the 1000 ppm limit exceeded 89.3 % of the school-day time (F-0038). Across the European SINPHONIE campaigns the mean exposure of schoolchildren was 1433 ppm, ranging from 269 ppm to 4957 ppm (F-0039).
Is a carbon dioxide monitor enough to judge classroom air?
It is the best single indicator of how much air is being exchanged, and it is cheap to measure continuously. It says nothing about particulate matter from outside or about volatile compounds from furniture and cleaning — those need their own measurement.
Sources
- Claim C-0018: In classrooms, mechanical ventilation may lower indoor carbon dioxide: two independent measurement campaigns found lower concentrations where central mechanical ventilation was present than where it was not.
- Finding F-0038: “Study results showed that the recommended limit of 1000 ppm CO2 was exceeded 89.3% of the time.” (CKB 0336, p. 1)
- Finding F-0039: “In the SINPHONIE campaigns, CO2 exposure ranged from 269 ppm to 4,957 ppm among schoolchildren, the mean being 1,433 ppm and the median 1,257 ppm.” (CKB 0012, p. 52)
- Finding F-0040: “About 11% of the SINPHONIE classrooms featured mechanical ventilation. In these classrooms the concentration of CO2 was significantly lower than in classrooms without mechanical ventilation (mean values 1,087 ppm and 1,510 ppm, respectively).” (CKB 0012, p. 52)
- Finding F-0041: “The average school-day CO2 concentration was 841 ppm (SD: 405 ppm) and the 99.9th percentile of daily maxima was 5080 ppm.” (CKB 1363, p. 1)
- Finding F-0042: “The average school-day CO2 concentration was 841 ppm (SD: 405 ppm) and the 99.9th percentile of daily maxima was 5080 ppm.” (CKB 1363, p. 1)
- Finding F-0043: “Elevated levels occurred in all buildings, although schools with central mechanical ventilation had lower concentrations and variability than schools without.” (CKB 1363, p. 1)
- SINPHONIE Schools Indoor Pollution and Health Observatory Network in Europe - Final Report… (2014). doi:10.2788/99220 CKB 0012
- Klavina Carbon dioxide as indoor air quality indicator in renovated schools in Latvia… (2016). CKB 0336
- Ge Decision tools for schools using continuous indoor air quality monitors: a case study of CO2 in Boston Public Schools (2025). Lancet Reg Health Am. doi:10.1016/j.lana.2025.101148 CKB 1363
- Building Bulletin 101: Guidelines on ventilation, thermal comfort and indoor air quality in schools. UK Department for Education, 2018.
- Umweltbundesamt: Gesundheitliche Bewertung von Kohlendioxid in der Innenraumluft. Bundesgesundheitsblatt 51, 2008.
- ANSI/ASHRAE Standard 62.1: Ventilation and Acceptable Indoor Air Quality.
CKB = document number in the Coridum Knowledge Base, our curated library of peer-reviewed studies. Follow the DOI for the original paper.
Cite this page
Coridum Research. How much CO₂ is too much in a classroom? Coridum Knowledge A-0001, 8 September 2026. https://coridum.com/k/A-0001/