The Internal Radiation Hazard An Introduction to Radiation

  • Slides: 29
Download presentation
The Internal Radiation Hazard An Introduction to Radiation Protection 6 e 2012 © 2012

The Internal Radiation Hazard An Introduction to Radiation Protection 6 e 2012 © 2012 Martin, Harbison, Beach, Cole/Hodder Education An Introduction to Radiation Protection 6 e © Martin, Harbison, Education

Introduction • Routes of Entry • Modelling and dose coefficients • Methods of protection

Introduction • Routes of Entry • Modelling and dose coefficients • Methods of protection – – – facility design containment area designation procedures PPE • Contamination monitoring • Personal monitoring An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Routes of Entry An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison,

Routes of Entry An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Inhalation • From airborne contamination • Proportion of radioactive material deposited in the and

Inhalation • From airborne contamination • Proportion of radioactive material deposited in the and remainder is exhaled is lungs • Some of the material in the lungs is brought up and swallowed • Some is absorbed directly from the lungs into the bloodstream and goes to target organs An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Ingestion • From contamination on foodstuffs, hands etc • Some will be absorbed into

Ingestion • From contamination on foodstuffs, hands etc • Some will be absorbed into the bloodstream and goes to target organs • Reminder will be excreted in faeces An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Modelling • Dose received is dependent on: – Specific radionuclide – Intake pathway –

Modelling • Dose received is dependent on: – Specific radionuclide – Intake pathway – Chemical and physical form – Particle size • Effective decay constant in the body λeff = λrad + λbio λrad = radioactive decay constant, λbio = biological decay constant • Effective half life in the body 1 = teff 1 + trad 1 tbio An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Elimination Curve for I-131 e -λbiot e -λtott e -λradt Biological half life ≈

Elimination Curve for I-131 e -λbiot e -λtott e -λradt Biological half life ≈ 80 days Radiological half life ≈ 8 days An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Elimination Curve for Cs-134 e -λradt e -λbiot e -λtott Biological half life ≈

Elimination Curve for Cs-134 e -λradt e -λbiot e -λtott Biological half life ≈ 110 days Radiological half life ≈ 2 years An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Elimination Curve for Po-210 e -λradt e -λbiot e -λtott Biological half life ≈

Elimination Curve for Po-210 e -λradt e -λbiot e -λtott Biological half life ≈ 50 days Radiological half life ≈ 140 days An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Dose Rate Curve Most of intake has reached the target organ Dose rate decreases

Dose Rate Curve Most of intake has reached the target organ Dose rate decreases exponentially e -λtott Nuclide transported to organ Area under curve = committed equivalent dose An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Dose Rate Curve • Committed equivalent dose is defined as dose received following the

Dose Rate Curve • Committed equivalent dose is defined as dose received following the intake for 50 years for adults and 70 years for children An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Dose Per Unit Intake • Values given in ICRP 68 (workers) and ICRP 72

Dose Per Unit Intake • Values given in ICRP 68 (workers) and ICRP 72 (public) Radionuclide H-3 Pu-239 Compound Effective Dose Coefficient (Sv/Bq) Inhalation Ingestion Tritiated water 1. 8 x 10 -11 Hydrogen gas 1. 8 x 10 -15 - Oxides and hydroxides 3. 2 x 10 -5 2. 5 x 10 -7 All other compounds 8. 3 x 10 -6 9. 0 x 10 -9 Values for a worker, 5 μm particle size An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Methods of Protection • Eliminate use • Minimize activity • Containment • Procedures •

Methods of Protection • Eliminate use • Minimize activity • Containment • Procedures • Use of personal protective equipment (PPE) • Good housekeeping An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Facility Design • New facilities should be designed to be easily decontaminated – Good

Facility Design • New facilities should be designed to be easily decontaminated – Good clean finish with no gaps in which contamination can accumulate – Covings at all angles to walls, ceilings to walls and floors to walls – Non porous materials – gloss paint, sheet PVC – Work surfaces made of non-porous materials e. g. melamine, PVC, stainless steel An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Facility Design • Air flow from low contamination to high contamination • Ventilation, use

Facility Design • Air flow from low contamination to high contamination • Ventilation, use of HEPA filter units etc • Gaseous discharges – location of discharge • Containment • Work being done within the facility • Decommissioning An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Containment • Fume cupboards • Glove boxes • Bespoke containment e. g. Modu. Con.

Containment • Fume cupboards • Glove boxes • Bespoke containment e. g. Modu. Con. TM Modular Containment System • Tented structures An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Containment • Facilities should be design with various levels of containment where practicable, especially

Containment • Facilities should be design with various levels of containment where practicable, especially if the radiation risks are significant Schematic diagram showing four levels of containment An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Containment – Glove Boxes • Mainly used when working with alpha or beta emitters

Containment – Glove Boxes • Mainly used when working with alpha or beta emitters • Maintained at lower pressure relative to main work area so that air flows inwards if a leak develops • Filtered inlet and extract air Schematic diagram of a glove box An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Area Designation • Uncontrolled (non-active) – No potential for radioactive contamination • Supervised Contamination

Area Designation • Uncontrolled (non-active) – No potential for radioactive contamination • Supervised Contamination – Low potential for contamination but need to keep under review • Controlled Contamination – Contaminated to greater or lesser extent and requiring appropriate precautions and protection measures An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Procedures • Radiation safety arrangements (rules) for working in contamination areas – No eating,

Procedures • Radiation safety arrangements (rules) for working in contamination areas – No eating, drinking, smoking – Wounds to be covered before entering areas – Wounds sustained in area to be reported immediately and treated accordingly • Barrier procedures • Work procedures • Pre work safety talks An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Use of PPE • Selection should be based on nature and amount of contamination

Use of PPE • Selection should be based on nature and amount of contamination and also the working environment • Low risk – lab coat, overshoes and gloves • Medium risk – coveralls, overshoes (taped), respiratory protection • High risk – pressurised suits An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Contamination Monitoring • Instruments need to be sensitive, generally use scintillation materials e. g.

Contamination Monitoring • Instruments need to be sensitive, generally use scintillation materials e. g. zinc sulphide for alpha, plastic phosphor for beta • Consist of a probe attached to a ratemeter - measure in counts per second (cps) • Need to know conversion factors to go from directly from cps to Bqcm-2 when direct monitoring • Beta probes respond to gamma radiation An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Smear Surveys • Used to: – Detect very low levels of contamination – Monitor

Smear Surveys • Used to: – Detect very low levels of contamination – Monitor for contamination in an area of high radiation background – Monitor for nuclides that are difficult to detect using direct methods e. g. H-3, C-14 – Establish if contamination is loose or fixed – Monitor areas that are inaccessible with instruments An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Smear Surveys • If a filter paper is smeared over a specific area e.

Smear Surveys • If a filter paper is smeared over a specific area e. g 300 cm 2 or 1000 cm 2 and then counted in a detecting system of known efficiency the surface contamination level can be calculated Contamination Level (Bqcm-2) 100 1 100 = Cc x E x A x E c F where Cc = background corrected count rate (cps) Ec = percentage efficiency of the counting system A = area smeared (cm 2) EF = percentage pick up by paper, usually 10% An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Air Monitoring • Carried out in areas where airborne contamination may occur e. g.

Air Monitoring • Carried out in areas where airborne contamination may occur e. g. by: – Disturbing surface contamination – Allowing liquid contamination to dry out – Carrying out dry, dusty operations e. g. cutting, grinding An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Air Monitoring • If a known volume of air is sampled and the sample

Air Monitoring • If a known volume of air is sampled and the sample paper is counted in a detecting system of known efficiency the particulate airborne contamination level can be calculated Contamination Level (Bqm-3) 100 1 = Cc x E x V c where Cc = background corrected count rate (cps) Ec = percentage efficiency of the counting system V = volume sampled (m 3) An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Personal Monitoring • May need to do in addition to area monitoring if: –

Personal Monitoring • May need to do in addition to area monitoring if: – the dose per unit intake is high e. g. plutonium – a nuclide is difficult to detect by monitoring – there is a significant risk that individuals could receive an intake – there has been an accident An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Personal Monitoring • Whole body monitoring for emitters e. g. Co-60 gamma • Can

Personal Monitoring • Whole body monitoring for emitters e. g. Co-60 gamma • Can also target specific organs e. g. thyroid counter for I-131 • Excretion (urine or faecal) monitoring for alpha/beta emitters e. g. Pu-239 • Personal air sampling • Can also take nasal swabs following a suspected intake An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education

Summary • Routes of Entry • Modelling and dose coefficients • Methods of protection

Summary • Routes of Entry • Modelling and dose coefficients • Methods of protection – – – facility design containment area designation procedures PPE • Contamination monitoring • Personal monitoring An Introduction to Radiation Protection 6 e © 2012 Martin, Harbison, Beach, Cole/Hodder Education