🌿 Radon measurement in buildings

Environmental PN-EN ISO 11665-4/-8

Measurement of average radon (²²²Rn) concentration in indoor air of buildings using passive detectors (alpha tracks). Mandatory testing in elevated risk zones.

Overview

Radon-222 is a natural radioactive noble gas, a decay product of radium-226 in the Earth's crust. Radon penetrates buildings through foundation cracks, pipes, and fractures, accumulating in basements and ground floors. It is the second (after smoking) cause of lung cancer — WHO estimates 3–14% of lung cancer deaths are due to radon.

EURATOM Directive 2013/59 establishes a reference level of 300 Bq/m³ for existing buildings. In Poland, radon measurements are regulated by Atomic Law and regulations of the President of PAA. Measurement is performed with passive CR-39 type detectors (alpha track detectors) exposed for 2–12 months to obtain reliable average concentration.

Method principle

A passive detector (CR-39 film in diffusion housing) is exposed in a room for 2–12 months. Alpha particles emitted by radon and its progeny (²¹⁸Po, ²¹⁴Po) leave microscopic tracks in the CR-39 film. After exposure, the film is etched in NaOH (6 mol/L, 90°C, 6 h), which enlarges the tracks to sizes visible under microscope. The number of tracks per cm² is proportional to radon concentration × exposure time. Concentration is calculated from calibration (detector calibration factor).

Applications

Key parameters

ParameterValue
Measurement range20–10,000 Bq/m³
Detection limit20 Bq/m³ (at 3 months exposure)
Reference level (EU)300 Bq/m³ (existing buildings)
Exposure time2–12 months (recommended ≥3 months)
Measurement uncertainty±15–25% (at concentration >100 Bq/m³)

Standard

Standard number
PN-EN ISO 11665-4:2020, PN-EN ISO 11665-8:2020
Title (PL)
Pomiary promieniotwórczości w środowisku — Powietrze: radon-222 — Część 4: Zintegrowana metoda pomiaru średniego stężenia aktywności z użyciem pasywnych próbników
Title (EN)
Measurement of radioactivity in the environment — Air: radon-222 — Part 4: Integrated measurement method for determining average activity concentration using passive sampling

Step-by-step procedure

1. Detector placement

Place 2 detectors on lowest occupied floor (bedroom, living room). Height 0.5–2 m, away from windows and ventilation.

⏱ Time: 15 min

2. Exposure

Leave detectors for 3–12 months. Record start and end dates with 1-day accuracy.

⏱ Time: 3–12 months

3. Detector retrieval

Close detectors in housing and send to analytical laboratory.

⏱ Time: 10 min

4. Chemical etching

CR-39 film etched in 6 mol/L NaOH, 90°C, 6 h. After etching rinse in distilled water and dry.

⏱ Time: 7 h • 🌡 Temperature: 90°C

5. Track counting

Count alpha tracks under microscope (automatically or manually). Typically 3–10 fields of view per detector.

⏱ Time: 15 min/detector

6. Concentration calculation

C [Bq/m³] = (track density − background) / (calibration factor × exposure time). Result as annual average concentration.

⏱ Time: 10 min

Required equipment and apparatus

EquipmentExampleIndicative price
CR-39 passive detectorsRadosys RS Radon, NRPB/PHE Track-etch, Gammadata Rapidos30–80 PLN/pc.
Etching-counting systemRadosys RSV-8, TASL Radometer (automatic)50,000–150,000 PLN
Water bath with thermostat90°C ± 1°C, for CR-39 etching3,000–8,000 PLN
Microscope with automatic countingOlympus BX53 with camera + software30,000–80,000 PLN

Reagents, media and consumables

ReagentCASDetails
Sodium hydroxide NaOH1310-73-26 mol/L solution (240 g/L) for CR-39 etching
Distilled waterFor film rinsing after etching

Health and safety (OHS)

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