Turn PM10 readings into clear air quality scores. Understand risks using standard breakpoint interpolation quickly. Track pollution levels, export reports, and act wisely now.
This calculator uses linear interpolation between concentration breakpoints to compute the Air Quality Index:
Values below use µg/m³ and 24-hour breakpoints for the air index.
| PM10 (µg/m³) | AQI Range | Category | Example Use |
|---|---|---|---|
| 0 – 54 | 0 – 50 | Good | Clean day after rainfall |
| 55 – 154 | 51 – 100 | Moderate | Typical urban background |
| 155 – 254 | 101 – 150 | USG | Dusty roadside conditions |
| 255 – 354 | 151 – 200 | Unhealthy | Construction activity nearby |
| 355 – 424 | 201 – 300 | Very Unhealthy | Regional haze episode |
| 425 – 504 | 301 – 400 | Hazardous | Severe pollution event |
| 505 – 604 | 401 – 500 | Hazardous | Extreme dust storm |
| PM10 (µg/m³) | Estimated AQI | Category |
|---|---|---|
| 35 | 32 | Good |
| 85 | 69 | Moderate |
| 180 | 116 | Unhealthy for Sensitive Groups |
| 300 | 170 | Unhealthy |
| 400 | 264 | Very Unhealthy |
| 480 | 353 | Hazardous |
PM10 describes inhalable particles with aerodynamic diameter up to 10 micrometers. Typical sources include road dust, construction activity, sea spray, agricultural soil, and combustion residue. Because particles can travel, a single reading can reflect neighborhood emissions and regional transport together.
Monitors commonly report PM10 in µg/m³; some datasets use mg/m³. This tool converts mg/m³ to µg/m³ by multiplying by 1000. AQI breakpoints here are based on a 24‑hour concentration. If you only have hourly values, interpret the output as a reference indicator, not a regulatory result.
The index spans 0 to 500 and is mapped from 0 to 604 µg/m³ for PM10. The concentration bands used are 0–54, 55–154, 155–254, 255–354, 355–424, 425–504, and 505–604 µg/m³. Each band corresponds to an AQI segment: 0–50, 51–100, 101–150, 151–200, 201–300, 301–400, and 401–500.
Most concentrations fall between breakpoint endpoints, so the calculator applies linear interpolation. It scales your concentration position within its band to the matching AQI segment. This produces a smooth AQI progression rather than abrupt jumps at breakpoint boundaries, and the final AQI is rounded to a whole number.
Categories summarize risk bands: Good (0–50), Moderate (51–100), Unhealthy for Sensitive Groups (101–150), Unhealthy (151–200), Very Unhealthy (201–300), and Hazardous (301–500). Use the guidance text as general planning support. For official alerts, follow your local authority’s messaging and standards.
Before converting, confirm that the reading is time-aligned and quality-controlled. Watch for negative values, sensor warm-up spikes, and sudden step changes after maintenance. If you are using low-cost sensors, compare against a nearby reference station when possible and use consistent averaging windows.
AQI is most useful for comparing time periods and communicating severity quickly. For trend work, keep the same averaging period and unit, then track daily medians or rolling averages. When exporting, include timestamp, concentration in µg/m³, AQI, and category so your report remains auditable.
Use the computed AQI to trigger operational decisions such as rescheduling outdoor work, adjusting ventilation schedules, or issuing community advisories. Pair the result with meteorology notes like wind and dryness, since dust and resuspension can dominate PM10 during calm, dry conditions.
PM10 is particulate matter up to 10 µm. Higher levels can irritate airways and worsen respiratory symptoms. It is also a practical indicator of dust events and coarse pollution sources.
Use a 24‑hour average when possible, because the breakpoint table is 24‑hour based. Hourly values can be converted for context, but they may not match official reporting.
Yes. If PM10 exceeds 604 µg/m³, the displayed AQI is capped at 500. This prevents extrapolating beyond the published index range.
Yes. Select mg/m³ and the tool converts it to µg/m³ automatically using 1 mg/m³ = 1000 µg/m³, then applies the breakpoint calculation.
Negative concentrations are not physically meaningful for this use and are rejected. If data is missing, leave the field blank and gather a valid measurement before calculating.
Agencies may use different standards, rounding rules, update schedules, or averaging definitions. Always compare against the same methodology used by the official source.
After calculation, use “Download CSV” for a spreadsheet row or “Download PDF” for a printable report. Both include timestamp, concentration, AQI, and category.
Important Note: All the Calculators listed in this site are for educational purpose only and we do not guarentee the accuracy of results. Please do consult with other sources as well.