NRPP RMS study materials
NRPP RMS study resources

NRPP RMS cheat sheet

NRPP RMS · Keep the key ideas within reach.

Quick reference

Radon Measurement Professional Scope

  • Radon is a colorless, odorless, radioactive noble gas; the primary health concern is inhalation of its short-lived decay products (polonium-218 and polonium-214), which emit alpha particles in the lung.

  • The U.S. action level and EPA-recommended mitigation trigger is 4 pCi/L; the WHO reference level is 100 Bq/m3 (about 2.7 pCi/L).

  • Unit conversions: 1 pCi/L = 37 Bq/m3; 1 WL (working level) = 100 pCi/L at equilibrium, and equilibrium ratio (ER) = actual WL divided by potential WL.

  • Short-term tests are typically 2-90 days; closed-building conditions require 12 hours before the test begins and must be maintained for the full exposure period (doors and windows closed, no fans or dryers venting air).

  • Device types: passive (charcoal, alpha track, electret ion chamber, liquid scintillation) versus active/continuous monitors; CRM tests need a minimum 48-hour exposure and hourly data.

  • Test placement: lowest livable level, 20 inches (50 cm) above the floor, at least 12 inches (30 cm) from exterior walls, and at least 4 inches (10 cm) from other objects.

  • Duplicate measurements (simultaneous side-by-side devices) and blank/spike controls assess precision and bias; a duplicate pair should be within 25 percent of their mean or 0.3 pCi/L, whichever is larger.

  • The CRM and electret measurement standards are ANSI/AARST MS-PC (continuous monitors) and MS-IM (electret ion chambers); MS-PC requires annual calibration and a control chart with a known-source spike every 30 days.

  • Long-term tests run more than 90 days and better represent the annual average; if a short-term test is 4 pCi/L or higher, a follow-up test (short- or long-term) is recommended before mitigation is decided.

Quick reference

Radon Mitigation and Soil Gas

  • The most common mitigation method is active soil depressurization (ASD): a suction point through the slab (sub-slab) or through a sump, a sealed piping run, and a continuously operating fan venting above the roof.

  • The vent stack must discharge above the roofline, at least 10 feet above grade and 10 feet from any window, door, or air intake, and must be labeled as a radon vent.

  • The post-mitigation retest is performed within 30 days of system activation (no sooner than 24 hours after start-up) under closed-building conditions; a passing result is below 4 pCi/L, with a goal of 2 pCi/L or less.

  • A system failure indicator (u-tube manometer or a system monitor/alarm) must be visible and labeled; the manometer reading should be recorded at installation to serve as the baseline for future checks.

  • Sub-slab communication is verified with a pressure-field extension test (PFE): a pressure differential of at least 50 Pa (0.2 inches water column) is the usual target at the farthest test hole from the suction point.

  • A depressurization field test (DFT) can be used on a diagnostic hole to confirm pressure field extension; diagnostic work should precede installation to size the fan and number of suction points.

  • The maximum radon concentration in the vent stack is typically several thousand pCi/L; the fan should be rated for continuous duty and the system must be sized so that the stack velocity is adequate, generally 20-30 feet per second at the fan.

  • For schools and large buildings, ANSI/AARST MA-MFLB (large building) and MAH (multifamily) standards govern design; HVAC pressure differentials and combustion appliance backdrafting must be evaluated before and after ASD installation.

  • Mitigation by sealing alone is not an approved stand-alone method; sealing is a supplemental measure used with ASD, and the system must not create a health or safety hazard (e.g., backdrafting of combustion appliances).