Methodology, data sources, and update policy

This site is designed to help people interpret AQI and make air-quality decisions. The estimate is intentionally simple enough to be understandable, while still tied to recognizable public methodology.

Reviewed and updated: August 13, 2026

Interactive formula explorer

Follow the estimate one step at a time

Start with a PM2.5 AQI or a direct PM2.5 reading, choose the exposure time, and inspect every value used in Berkeley Earth's rough population-level health-impact comparison.

Explore the comparison assumption

The site default is 22 µg/m³ for 24 hours. Changing this field is a sensitivity exercise; it does not change the production calculator or the underlying Berkeley Earth reference.

Berkeley Earth comparison

2.52 cigarette-equivalents

This is a rough population-level health-impact equivalence for risk communication. It does not measure cigarettes smoked or predict any individual's exposure, diagnosis, or health outcome.

  1. Step 1 · concentration

    AQI 150 → 55.4 µg/m³ PM2.5

    Interpolation band: AQI 101150 / PM2.5 35.555.4 µg/m³.

  2. Step 2 · concentration-hours

    55.4 × 24 = 1,329.6 µg·h/m³

  3. Step 3 · comparison reference

    22 × 24 = 528 µg·h/m³

  4. Step 4 · ratio

    1,329.6 ÷ 528 = 2.52

1. AQI to PM2.5

The calculator first converts a PM2.5 AQI into an estimated PM2.5 concentration using the current U.S. EPA breakpoints: 0–9.0, 9.1–35.4, 35.5–55.4, 55.5–125.4, 125.5–225.4, and 225.5–325.4 µg/m³ for AQI bands through 500. AQI is easier to look up, while PM2.5 is the concentration used by the Berkeley Earth comparison.

Values above AQI 500 are outside the standard display scale. When such a value is entered, the site follows AirNow's documented approach of extending the 301–500 PM2.5 slope and labels the result as an extrapolation.

Primary references: the current EPA AQI breakpoint table and AirNow technical assistance document, updated May 2026.

2. PM2.5 to a rough health-impact equivalence

After estimating PM2.5, the site applies Berkeley Earth's rough population-level health-impact equivalence as a risk-communication heuristic. Its rule of thumb treats 22 µg/m³ sustained for one day as approximately one cigarette-equivalent in health impact. It does not measure cigarettes smoked or predict an individual's exposure, diagnosis, or health outcome.

Primary reference: Berkeley Earth's air pollution and cigarette equivalence framing.

3. Direct PM2.5 mode

The calculator also accepts PM2.5 directly. In that mode, the rough comparison keeps the entered PM2.5 concentration at its original precision, while the AQI conversion separately follows EPA's requirement to truncate PM2.5 to one decimal before interpolation.

This preserves the source reading for the concentration-time calculation without changing the EPA AQI calculation rule.

4. What the estimate is good for

Comparing one day or one scenario against another.
Making practical decisions for commuting, workouts, kids, or smoke events.
Seeing how repeated days can add up across a week.
Explaining air-quality risk in terms people can quickly grasp.

5. Live city data layer

City pages use EPA AirNow as a live enhancement layer where regional coverage and an API response are available. If the API is unavailable, rate-limited, unsupported for the city, or not configured in the deployment environment, the site falls back to a static planning baseline instead of failing open.

The live layer is designed as a lightweight utility feature, not a hard dependency.

6. Important limitations

  • The estimate is not a medical diagnosis and does not predict an individual health outcome.
  • AQI is pollutant-specific. An ozone, nitrogen dioxide, sulfur dioxide, or carbon monoxide AQI cannot be treated as a PM2.5 concentration; the conversion tools require a PM2.5 AQI or clearly label the PM2.5 assumption.
  • Real-world exposure changes with exertion, indoor leakage, masks, ventilation, and time spent in cleaner or dirtier microenvironments.

7. Update policy

We review the site when the calculator logic changes, when key methodology references materially change, or when new internal content is added. Supporting pages are updated to improve clarity, internal linking, and user decision value.

The city and scenario pages remain planning aids first. The live AQI layer is intended to improve utility, but users should still interpret rapidly changing smoke or pollution events conservatively and cross-check with local authorities when needed.