Becquerels to Sieverts Converter

Select a radionuclide and pathway, enter activity in becquerels, and get effective dose in sieverts using published ICRP coefficients.

Inputs

Effective dose (Sv) = Activity (Bq) × Dose coefficient (Sv/Bq)

Quick examples

Results

Select a nuclide, pathway, and activity, then press Calculate

Bq, Sv, and why nuclide choice matters

Becquerel (Bq)

One disintegration per second. It describes how active a source is, not how dangerous. A highly active source can be nearly harmless (short-lived, weak emitter) or very hazardous (long-lived, alpha emitter in organ tissue).

Sievert (Sv)

Effective dose, weighted for radiation type and organ sensitivity. 1 Sv = 1 J/kg × quality × tissue factors. The global annual background is about 2.4 mSv; occupational limits are typically 20 mSv/year.

Why nuclide matters

1 MBq of H-3 ingested gives roughly 18 µSv. The same activity of Po-210 ingested gives about 1,200 mSv — more than 60,000 times higher. Decay energy, radiation type, and organ uptake drive the difference.

Dose coefficients sourced from ICRP Publication 72 (1996) for adults. This tool is for educational purposes only — not for medical, regulatory, or occupational dose assessment.

Summary

Select a radionuclide and pathway, enter activity in becquerels, and get effective dose in sieverts using published ICRP coefficients.

How it works

  1. Select a radionuclide from the dropdown — common choices include I-131, Cs-137, H-3, Ra-226, and others.
  2. Choose an exposure pathway: ingestion (swallowing) or inhalation (breathing).
  3. Enter the activity in becquerels (Bq), kiloBq, MegaBq, etc.
  4. The tool multiplies activity by the ICRP effective dose coefficient (Sv/Bq) to produce effective dose.
  5. Results are shown in sieverts, millisieverts, microsieverts, and as a fraction of annual background dose.
  6. For precise regulatory or medical use, always consult authoritative ICRP/EPA publications and a qualified health physicist.

Use cases

  • Estimating committed effective dose from accidental radionuclide ingestion.
  • Education and training in radiation protection principles.
  • Cross-checking hand calculations in nuclear medicine or health physics coursework.
  • Comparing nuclide-specific dose contributions in environmental dose assessments.
  • Understanding why 1 Bq of different nuclides produces vastly different doses.
  • Rough screening of potential dose from food or water contamination incidents.

Frequently Asked Questions

Last updated: 2026-07-22 · Reviewed by Nham Vu