Air Purifier CADR and Indoor PM2.5 Calculator

Size a purifier and estimate indoor PM2.5 with outdoor leakage, deposition and indoor sources. See the steady level, cleaning time and animated particle balance.

#AHAM AC-1 #air purification #AQI #CADR #deposition #infiltration #mass balance #PM2.5

Use this air purifier room size calculator to estimate indoor PM2.5 during urban smog or wildfire smoke. It is designed for engineers, students and households comparing purifier capacity for one connected room. Enter a particle clean air delivery rate (CADR), and the calculator predicts both the concentration over time and the steady indoor level while outdoor particles continue to enter.

Start with the floor area and ceiling height. Use the entire connected space if doors remain open. Enter smoke or fine-particle CADR at the fan setting you will actually run; fan airflow alone is insufficient. For several purifiers operating in the same mixed space, add their CADRs. The metric/US unit switch converts room geometry. Select m³/h or CFM separately for CADR entry; the target requirement is reported in both. PM2.5 remains a mass concentration.

Next, enter outdoor PM2.5 and the indoor reading when the purifier starts, both in micrograms per cubic metre. Do not enter an AQI number in these fields. Choose your own indoor target. Outdoor air exchange, penetration and surface deposition are uncertain building parameters: the defaults are illustrative assumptions. Try a higher leakage rate and penetration of one to explore a less protected room. Set deposition to zero to avoid crediting an uncertain surface loss. Keep indoor emissions at zero after cooking or another source has stopped.

The CADR calculator uses a well-mixed particle mass balance. Outdoor infiltration and any continuous indoor emission add particles; air leaving, surface deposition and the purifier remove them. More clean air generally lowers the steady concentration, but ongoing outdoor entry prevents the level from falling to zero. The CADR threshold is the minimum needed to keep the steady indoor level at or below the chosen target. To cross the target from above in finite time, the steady concentration must be strictly below it. Zero CADR can satisfy this when natural removal already suffices; a positive threshold must be exceeded.

Wondering how long does an air purifier take to clean a room? Read the target result and the time curve, then press play to watch the schematic particles thin out. The separate 95% settling time means closing 95% of the gap to the final level; it does not mean removing 95% of all PM2.5. The purifier-off curve and CADR sweep show why room-size rules can disagree.

EPA’s 2018 room-sizing table is provided as a volume-adjusted benchmark alongside four-to-six equivalent clean air changes per hour. These comparisons cannot account for your actual leakage. AQI comparisons use US EPA May 2026 guidance or the India CPCB 2014 category scheme, checked on 25 October 2026. They describe PM2.5 alone, without the averaging or other pollutants required for official AQI reporting.

Health disclaimer: This is a screening model, not medical advice or a guarantee of safe air. A particle purifier does not remove carbon dioxide or carbon monoxide, and filtration does not replace necessary ventilation. Follow local smoke advisories, control indoor sources and verify results with a suitable monitor.

How it is calculated

For a constant-volume room, conservation of particle mass gives

dCdt=PλCo+SV−(λ+kd+QV)C.\frac{dC}{dt}=P\lambda C_o+\frac{S}{V}-\left(\lambda+k_d+\frac{Q}{V}\right)C.

Here V=AHV=AH, QQ is particle CADR, λ\lambda is outdoor air exchange, PP is penetration, kdk_d is deposition and SS is indoor emission. All rates use hours. Set J=PλCo+S/VJ=P\lambda C_o+S/V and r=λ+kd+Q/Vr=\lambda+k_d+Q/V; then C∞=J/rC_\infty=J/r and C(t)=C∞+(C0−C∞)e−rtC(t)=C_\infty+(C_0-C_\infty)e^{-rt}. The purifier-off curve uses r=λ+kdr=\lambda+k_d, including linear accumulation when that rate is zero.

For C0>CT>C∞C_0>C_T>C_\infty, first passage is t=ln⁡[(C0−C∞)/(CT−C∞)]/rt=\ln[(C_0-C_\infty)/(C_T-C_\infty)]/r. A target equal to the steady level is approached asymptotically. An initially satisfied target has first-passage time zero; a warning identifies a later rise above it. The steady CADR threshold is QT=max⁡[0,V(J/CT−λ−kd)]Q_T=\max[0,V(J/C_T-\lambda-k_d)]. When starting above the target, finite-time crossing requires C∞<CTC_\infty<C_T. Zero CADR can satisfy this when natural removal already keeps the steady concentration strictly below the target; a positive CADR threshold must be exceeded. The 95% settling time is ln⁡(20)/r\ln(20)/r.

The balance is derived here from conservation. EPA Guide (2018), attached PDF page 3, provides the room-sizing benchmark: 65 cfm per 100 ft² at 8 ft implies 4.875 equivalent clean air changes per hour. Multiplying by actual volume adjusts for ceiling height. Four and six changes per hour are comparison scenarios, not regulatory requirements. Particle CADR is the performance metric named in ANSI/AHAM AC-1-2020; no standard test or product certification is performed here. Shaughnessy and Sextro (2006) discuss CADR and competing removal processes.

US PM2.5 sub-index comparisons truncate concentration to 0.1 µg/m³, interpolate EPA breakpoints, then round the index; values above 500 continue the hazardous segment, per EPA May 2026 guidance, pp. 13–15. India comparisons use CPCB Table 3.11, printed p. 35 (attached page 37): successive upper concentration cutoffs 30, 60, 90, 120 and 250 µg/m³. Fractional concentrations move to the next band immediately above each cutoff. Only categories are shown for India; no numeric value is invented for its open-ended Severe band.

Assumptions

One uniformly mixed room; fixed volume, CADR, outdoor concentration and source strength. Equal incoming and outgoing outdoor airflow. Penetration applies only to incoming particles; outgoing air carries the full indoor concentration. Deposition is an independent first-order sink, with no resuspension. CADR already includes filter efficiency; do not multiply it by HEPA efficiency again.

The default exchange rate 0.5 h⁻¹, penetration 0.8 and deposition 0.2 h⁻¹ are illustrative inputs, not literature-derived estimates for Delhi, Lahore, Dhaka or any particular building. Set them from measurements or test a range. Animated dots represent relative concentration on a fixed scale and their motion is illustrative, not a flow simulation.

Where it applies

Health disclaimer: Educational screening estimate, not medical advice, exposure certification, a safe re-entry time or a guarantee of health protection. A chosen target or a Good category does not prove indoor air is safe. Follow local public-health advice and consult a qualified health professional for individual concerns.

Suitable for approximate particle behaviour in one mixed room with constant conditions. Poor mixing, obstructed purifier airflow, adjoining rooms, changing wind, open doors, filter loading, humidity effects on monitors and intermittent cooking can cause large departures. Verify with a suitable PM2.5 monitor. CADR addresses particles; it does not establish removal of gases, CO₂ or CO. Avoid ozone-generating cleaners and maintain necessary ventilation. Installation or changes to ventilation/HVAC belong to a qualified person.

AQI is an outdoor-air reporting system: these instantaneous and steady PM2.5 comparisons are not an official daily AQI, a NowCast, an indoor limit or a complete multi-pollutant index. Rules used: US EPA May 2026 guidance (2024 PM2.5 breakpoints) and CPCB 2014 scheme; verified 25 October 2026. For compliance, check against the standard and rules in force.

References

  • US EPA (2018). Guide to Air Cleaners in the Home, 2nd ed., pp. 3 and 5. https://www.epa.gov/indoor-air-quality-iaq/guide-air-cleaners-home
  • Shaughnessy, R. J.; Sextro, R. G. (2006). What Is an Effective Portable Air Cleaning Device? A Review. Journal of Occupational and Environmental Hygiene 3:169–181. DOI:10.1080/15459620600580129. Cited for CADR context; full text was not used.
  • CDC. Guidelines for Environmental Infection Control in Health-Care Facilities (2003), Appendix B, Table B.1; web edition 11 January 2024. Source-free ideal mixing clearance reference only. https://www.cdc.gov/infection-control/hcp/environmental-control/appendix-b-air.html
  • US EPA (May 2026). Technical Assistance Document for the Reporting of Daily Air Quality – the AQI, EPA-403/B-26-003, pp. 13–15, Table 6. https://document.airnow.gov/technical-assistance-document-for-the-reporting-of-daily-air-quailty.pdf
  • CPCB (2014). National Air Quality Index, Final Report, Table 3.11, p. 35; attached PDF page 37. https://www.cpcb.gov.in/displaypdf.php?id=bmF0aW9uYWwtYWlyLXF1YWxpdHktaW5kZXgvRklOQUwtUkVQT1JUX0FRSV8ucGRm
  • AHAM. Air Filtration Standards: CADR and separate smoke, dust and pollen metrics. ANSI/AHAM AC-1-2020 is named for context. https://ahamverifide.org/ahams-air-filtration-standards/

Inputs

InputSymbolUnitDefault
Room floor area
Include the whole connected area served by this purifier.
A_roomm^225
Ceiling heightH_roomm2.7
CADR entry units
Choose the units in which you will enter CADR. The metric/US switch handles room geometry.
flow_unitsCubic metres per hour (m³/h)
Particle CADR at the fan speed used
Use smoke or fine-particle CADR, not fan airflow. Add CADRs of units serving this same mixed room.
Q_cleanm^3/h300
Particle CADR at the fan speed used
Use smoke or fine-particle CADR in CFM, not fan airflow. Enter the value for the fan setting you will run.
Q_cfmft^3/min176.573333
Outdoor PM2.5
Enter mass concentration, not an AQI number. Assumed constant throughout the run.
C_outug/m^3150
Indoor PM2.5 when purifier startsC_startug/m^3100
Chosen indoor PM2.5 target
A comparison target, not a declaration of safe air or a health recommendation.
C_goalug/m^315
Outdoor air exchange rate
Infiltration plus outdoor ventilation. 0.5 is an illustrative assumption, not a measured value for your room.
n_leakh^-10.5
Particle penetration fraction
Fraction of outdoor PM2.5 that penetrates the envelope (0–1). Use 1 for unfiltered open-window air; default 0.8 is illustrative.
P_in0.8
Surface deposition loss rate
First-order loss to room surfaces. Default is illustrative; use 0 for a conservative estimate without deposition.
k_deph^-10.2
Continuous indoor PM2.5 emission
Leave at zero after an indoor source has stopped. Cooking peaks and resuspension are not represented by a constant emission.
S_roomug/h0
Elapsed time · press ▶ to animate
Moves the room particles and the current concentration; charts and sizing are independent of playback.
t_viewmin20
AQI category comparison
PM2.5 concentration band only. This is neither an official daily AQI nor an AirNow NowCast.
aqi_scaleUS EPA (May 2026 guidance)

Results

With the default inputs above, the calc gives:

ResultValue
Indoor PM2.5 at elapsed time27.6 ug/m³
Steady indoor PM2.511.7 ug/m³
Time to chosen target38.2 min to target
CADR threshold for steady target222.75 m³/h
CADR threshold for steady target · CFM131.11 ft³/min
Purifier equivalent clean air changes4.44 h⁻¹
95% settling time toward steady level34.9 min
EPA volume-adjusted sizing benchmark329 m³/h
PM2.5 AQI comparison · elapsed time85 · Moderate
PM2.5 AQI comparison · steady level56 · Moderate

Checked against sources

Each case below was calculated by this calc and agrees with the value from its source (within the tolerance where one is shown).

CDC Table B.1: 99% clearance at 6 ACH

Source: CDC Appendix B Table B.1, 6 ACH: published 99% clearance time is 46 min. Source-free ideal mixing. Published integer is rounded; exact balance gives about 46.05 min. https://www.cdc.gov/infection-control/hcp/environmental-control/appendix-b-air.html

Inputs: Particle CADR at the fan speed used = 405 m³/h; Outdoor air exchange rate = 0 h⁻¹; Surface deposition loss rate = 0 h⁻¹; Chosen indoor PM2.5 target = 1 ug/m³; the others as above.

ResultSourceThis calc
Minutes to first reach target; undefined if never reached46 ± 0.15 min46.052 min

CDC Table B.1: 99.9% clearance at 12 ACH

Source: CDC Appendix B Table B.1, 12 ACH: 99.9% clearance is 35 min. Rounded published table; exact ideal solution is about 34.54 min. This checks the time transient using independently published values. https://www.cdc.gov/infection-control/hcp/environmental-control/appendix-b-air.html

Inputs: Particle CADR at the fan speed used = 810 m³/h; Outdoor air exchange rate = 0 h⁻¹; Surface deposition loss rate = 0 h⁻¹; Chosen indoor PM2.5 target = 0.1 ug/m³; the others as above.

ResultSourceThis calc
Minutes to first reach target; undefined if never reached35 ± 0.5 min34.539 min

EPA guide: 300 ft², 8 ft ceiling, 195 cfm

Source: EPA Guide to Air Cleaners in the Home (2018), p. 3 sizing row: 300 ft² requires 195 cfm at 8 ft. Expected CADR is the published 195 cfm converted to m³/h, not fitted to model. 1 ft = 0.3048 m exactly.

Inputs: Room floor area = 27.871 m²; Ceiling height = 2.438 m; Particle CADR at the fan speed used = 331.3 m³/h; the others as above.

ResultSourceThis calc
EPA volume-adjusted sizing benchmark331.3 m³/h331.3 m³/h
Purifier equivalent clean air changes4.875 h⁻¹4.875 h⁻¹

EPA worked example: PM2.5 35.9 gives sub-index 102

Source: EPA AQI Technical Assistance Document, May 2026, printed p. 15 (PDF page 20): worked example gives PM2.5 35.9 µg/m³ a sub-index of 102. https://document.airnow.gov/technical-assistance-document-for-the-reporting-of-daily-air-quailty.pdf

Inputs: Indoor PM2.5 when purifier starts = 35.9 ug/m³; Elapsed time · press ▶ to animate = 0 min; the others as above.

ResultSourceThis calc
US PM2.5 sub-index equivalent at elapsed time102102

EPA hazardous endpoint: 325.4 µg/m³ corresponds to 500

Source: EPA May 2026 AQI guidance Table 6 footnote 4 specifies 325.4 µg/m³ at index 500 for 24-hour PM2.5. Applying it to an instantaneous model concentration is an explicitly labelled comparison. https://document.airnow.gov/technical-assistance-document-for-the-reporting-of-daily-air-quailty.pdf

Inputs: Indoor PM2.5 when purifier starts = 325.4 ug/m³; Elapsed time · press ▶ to animate = 0 min; the others as above.

ResultSourceThis calc
US PM2.5 sub-index equivalent at elapsed time500500

EPA 195 CFM entry converts to model CADR

Source: EPA Guide (2018), p. 3: 300 ft² at 8 ft requires 195 cfm. This case enters the published value directly in CFM and verifies exact international-foot conversion and equivalent clean-air changes.

Inputs: CADR entry units = Cubic feet per minute (CFM); Particle CADR at the fan speed used = 195 ft³/min; Room floor area = 27.871 m²; Ceiling height = 2.438 m; the others as above.

ResultSourceThis calc
Particle CADR converted to model units331.3 m³/h331.3 m³/h
Purifier equivalent clean air changes4.875 h⁻¹4.875 h⁻¹

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