NO₂ to AQI Converter
Convert an NO2 concentration in parts per billion to its EPA Air Quality Index value and health category using official 1-hour breakpoint interpolation.
NO₂ to AQI Converter
Calculator
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Formula: AQI = Ilow + ((C-Clow)/(Chigh-Clow)) x (Ihigh-Ilow)
Worked example — AQI=73
Formula
AQI = Ilow + ((C-Clow)/(Chigh-Clow)) x (Ihigh-Ilow)
Map NO2 ppb to AQI via EPA breakpoint linear interpolation.
Worked Examples
Example 1: Moderate
Problem:NO2=75ppb,1hr,25C
Solution:BP 54-100,AQI 51-100 AQI=73, ug/m3=141
Result:AQI=73
Example 2: Unhealthy
Problem:NO2=450ppb,1hr,20C
Solution:BP 361-649,AQI 151-200 AQI=166
Result:AQI=166
Frequently Asked Questions
Which NO2 measurement does this converter expect?
The primary input is the NO2 concentration in parts per billion (ppb), measured as a 1-hour average per EPA AQI methodology. The averaging period matters because the EPA NO2 AQI is specifically defined for a 1-hour average; using a 24-hour or annual average will produce a breakpoint mismatch and an incorrect AQI value. Temperature is used only for the optional µg/m3 conversion displayed alongside the AQI and does not affect the AQI calculation itself. The AQI breakpoints embedded in NO₂ to AQI Converter follow EPA's 2018 technical assistance document: 0-53 ppb maps to Good (0-50 AQI), and the scale extends to Hazardous above 1250 ppb.
Why does entering a ug/m3 reading in the ppb field break the result?
The most critical unit error is entering µg/m3 in the ppb field, or vice versa, without performing the molecular weight conversion. At 25°C, 1 ppb NO2 equals approximately 1.88 µg/m3 (derived from the molar volume of 24.45 L/mol and NO2 molecular weight of 46.01 g/mol). Many low-cost sensors and European air quality reports express NO2 in µg/m3 while the EPA AQI system uses ppb exclusively; dividing a µg/m3 reading by 1.88 before entering it here is essential. Also confirm that your monitor reports a 1-hour average rather than an 8-hour or 24-hour average, as the NO2 breakpoints are averaging-period specific.
How can I reduce my environmental impact based on these results?
To reduce personal NO2 exposure when the AQI is elevated, start with indoor sources, since unvented gas cooking and unflued heaters can push kitchen NO2 above outdoor levels; running an extractor hood vented to the outside addresses that directly. Note that HEPA media captures particles only and does not remove NO2 at all; it is the activated carbon or chemisorbent stage of a filter that adsorbs the gas, and its performance depends on media mass, airflow and how long the cartridge has been in service, so treat filtration as a supplement to ventilation rather than a substitute. Outdoors, avoiding high-traffic corridors and staying away from intersections during rush-hour peaks cuts exposure significantly because NO2 concentrations drop sharply with distance from roadways. Timing ventilation and window-opening to morning or late evening when traffic volumes are lower also helps. For cyclists and pedestrians, routing through parks or side streets rather than arterial roads measurably reduces cumulative daily dose.
What is the difference between NO, NO2 and NOx when reading an AQI concentration in ppb?
Combustion mainly emits nitric oxide, NO, which is then oxidised in the atmosphere to nitrogen dioxide, largely by reaction with ozone and peroxy radicals. NOx is the sum of the two and is what emission inventories and permits normally regulate. Only nitrogen dioxide has its own ambient standard and AQI sub-index, so a roadside NOx figure in ppb cannot be converted to an AQI value directly; you need the measured NO2 fraction of that total concentration.
Why does NO2 fall off so sharply with distance from a road?
Roadside nitrogen dioxide is dominated by fresh local emissions rather than regional background, and plumes disperse rapidly through turbulent mixing as they move away from the kerb. Concentrations typically decline toward background within 100 to 200 metres of a busy highway. That steep gradient is why monitor siting changes the answer so much, and why near-road stations were added specifically to capture the short-term exposures the 1-hour standard addresses.
Why do the two lowest breakpoints sit at 53 and 100 ppb?
They are not arbitrary round numbers but come from the standards themselves. 53 ppb, that is 0.053 ppm, is the annual primary standard set in 1971, and 100 ppb is the 1-hour standard added in 2010 to address short-term near-road exposure. Since index 100 is pinned to the standard, the Moderate band runs from 54 to 100 ppb, and any value above index 100 signals that the 1-hour standard has been exceeded.
How does temperature affect the ug/m3 conversion but not the AQI?
The breakpoints are defined on a volume mixing ratio in parts per billion, which is independent of temperature and pressure, so changing the temperature input leaves the index unchanged. Mass concentration does change, because it depends on molar volume: 22.414 litres per mole at 0 degrees C expands to about 24.45 at 25 degrees C. At 25 degrees C one ppb of NO2, molar mass 46.01 g/mol, corresponds to roughly 1.88 ug/m3.
Why can a chemiluminescence monitor overstate the NO2 ppb used for the AQI?
The standard analyser measures nitric oxide by its chemiluminescent reaction with ozone and infers nitrogen dioxide by first passing the sample through a converter that reduces NO2 to NO. Heated molybdenum converters are not selective: they also reduce other oxidised nitrogen species such as peroxyacetyl nitrate and nitric acid, which are then counted as NO2. The bias grows in aged, photochemically processed air. Photolytic converters are selective and avoid it, so a molybdenum-based ppb reading can push the reported AQI into a higher band than the true NO2 concentration warrants.
How does the WHO guideline compare with the breakpoints used here?
This table is built on United States national ambient standards, so it reflects one regulatory framework rather than a universal health threshold. World Health Organization air quality guideline values for nitrogen dioxide are considerably stricter, which means air rated Good on this scale can still exceed the WHO guideline. When comparing cities internationally, state which index and which standard set you used, because a national index value is not portable between countries.
Can a low-cost electrochemical NO2 sensor be used with these breakpoints?
Electrochemical cells respond to nitrogen dioxide but also to ozone, usually with opposite sign, so better modules pair the NO2 cell with an ozone-scrubbing filter or a second cell whose signal is subtracted. Output additionally drifts with temperature, humidity and electrode age. Before feeding such a reading into this table, co-locate the unit beside a reference analyser to derive a correction, and average the sub-minute samples across a full clock hour, since the breakpoints are defined on a 1-hour mean.
References
Background & Theory
History
Reviewed for accuracy by Daniel Agrici, Founder & Lead Developer · Editorial policy
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