17-Phys-B1 Radiation Physics · May 2015
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
Paper format. 98-Phys-B1 Radiation Physics, National Examination May 2015 — a three-hour open-book examination in which any non-communicating calculator is permitted. The cover page states the exam has 7 questions worth a total of 100 points, of which only 80 points' worth need be answered for full marks; every question and sub-part is nonetheless answered in full below so the paper remains a complete study resource. The cover page also invites the candidate to submit a written statement of any assumptions made where a question is open to interpretation — this licence is used in Question 1(a) (proton-mass vs. hydrogen-atom-mass convention), Question 3(d) (single effective attenuation coefficient for the polychromatic X-ray beam) and Question 5(c) (reading "the body" as the thyroid uptake compartment, consistent with the biological half-life given). The exam's own page-6 marking-scheme summary is internally inconsistent for two questions (it prints "15 points" for both Q2 and Q3, but their own per-sub-part marks, given beside each sub-part on the question pages, sum to 18 and 17 respectively); the sub-part marks are used below since only that reading makes the paper's own stated 100-point total add up exactly ($12+18+17+18+18+10+7=100$).
Reference texts. K. S. Krane, Introductory Nuclear Physics (nuclear masses and binding energy, radioactive decay); F. H. Attix, Introduction to Radiological Physics and Radiation Dosimetry (X-ray production, photon attenuation); J. R. Cember and T. E. Johnson, Introduction to Health Physics, 5th ed. (internal dosimetry, effective half-life, shielding, radiation survey practice); J. E. Turner, Atoms, Radiation, and Radiation Protection, 3rd ed. (radiation interactions, detectors, health-physics standards).
Question text not reproduced: the examination questions are © Engineers and Geoscientists BC. Open the official past paper (linked at the top of this page) to read the question, then follow the worked solution below.
Given. An inhabited town adjacent to an abandoned uranium mine, with public concern over perceived elevated radiation levels; the deliverable is a one-page memorandum outlining a survey plan.
Find. A structured monitoring plan: what pathways/media need surveying, what instruments and sampling protocols to use, and against what regulatory benchmarks the results should be judged.
Approach. Work through the standard uranium-mine legacy-site exposure pathways — direct external gamma, radon and its progeny, surface/soil contamination, and water — and match each to an appropriate Canadian (CNSC/Health Canada) survey method and benchmark, then present the whole plan in memo form.
To: [Supervisor, Radiation Protection Bureau] From: [Surveying Officer] Re: Proposed radiation survey plan — abandoned uranium mine near [Town]
1. Purpose and scope. This memo proposes a baseline environmental radiation survey of the town and the abandoned mine site to respond to the mayor's concern, establish whether public exposure exceeds Canadian regulatory limits, and identify any remediation or ongoing monitoring needs. The survey will cover four exposure pathways: direct external gamma radiation, radon gas and its short-lived progeny, surface/soil contamination, and surface/groundwater quality.
2. External gamma survey. Perform a walkover gamma dose-rate survey using a calibrated portable scintillation or GM survey meter, on a systematic grid covering the town, the mine site itself (waste rock piles, tailings, adits), and undisturbed background reference locations well outside any plausible influence of the mine. Record dose rate ($\mu$Sv/h) with GPS-tagged locations to build a contour map, and flag any location whose dose rate is statistically elevated above the local background reference.
3. Radon and radon-progeny survey. Uranium mine sites and their tailings are major radon (${}^{222}$Rn) sources. Deploy passive integrating radon detectors (alpha-track or activated-charcoal canisters, minimum 90-day integration where feasible) in a representative sample of homes and other occupied buildings in the town, particularly those closest to the mine and those with basements or slab-on-grade construction. Compare results to the Health Canada guideline of 200 Bq/m$^3$ annual average indoor radon; any building at or above this level triggers follow-up and mitigation guidance.
4. Surface and soil survey. Collect soil samples on a grid across the mine site, tailings/waste-rock areas, and the town (including any areas where mine material may have been used as fill or aggregate), and analyze for uranium, radium-226 and daughter-product activity concentrations by gamma spectroscopy/alpha spectrometry. Perform surface swipe (smear) surveys of accessible mine structures for removable alpha/beta contamination.
5. Water survey. Sample the town's drinking-water supply (wells and any surface-water intake) and any surface water draining the mine site, analyzing for dissolved uranium and radium-226, compared against Health Canada's Guidelines for Canadian Drinking Water Quality (uranium maximum acceptable concentration 0.02 mg/L).
6. Instrumentation and QA. All survey meters and laboratory analyses will use instruments with current calibration traceable to a national standard, with field blanks, duplicate samples, and a documented chain of custody for every sample.
7. Benchmarks and next steps. All results will be compared against the CNSC Radiation Protection Regulations public dose limit (1 mSv/year above background) and the Health Canada radon and drinking-water guidelines noted above. A summary report with recommendations — further monitoring, access restriction, or remediation, as warranted — will follow within [X weeks], with results communicated transparently to the mayor and residents.
| Pathway | Method | Benchmark |
|---|---|---|
| External gamma | Grid walkover survey, portable dose-rate meter | Compared to local background |
| Radon | Passive integrating detectors in occupied buildings | Health Canada 200 Bq/m$^3$ |
| Soil / surface contamination | Soil sampling + gamma/alpha spectrometry; smear surveys | Site-specific background |
| Water | Well/surface-water sampling for U, Ra-226 | Health Canada 0.02 mg/L U |
| Overall public dose | Sum of pathway contributions | CNSC 1 mSv/y above background |