Acute Radiation Syndrome: a Fact Sheet for Physicians
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RADIATION EFFECTS and SOURCES What Is Radiation? What Does Radiation Do to Us? Where Does Radiation Come From?
RADIATION EFFECTS and SOURCES What is radiation? What does radiation do to us? Where does radiation come from? United Nations Environment Programme RADIATION EFFECTS and SOURCES What is radiation? What does radiation do to us? Where does radiation come from? United Nations Environment Programme DISCLAIMER This publication is largely based on the findings of the United Nations Scientific Committee on the Effects of Atomic Radiation, a subsidiary body of the United Nations General Assembly and for which the United Nations Environment Pro- gramme provides the secretariat. This publication does not necessarily r epresent the views of the Scientific Committee or of the United Nations Environment Programme. The designations employed and the presentation of the material in this publica- tion do not imply the expression of any opinion whatsoever on the part of the United Nations Environment Programme concerning the legal status of any country, territory, city or area or of its authorities, or concerning delimitation of its frontiers or boundaries. This publication may be reproduced in whole or in part and in any form for educational or non-profit purposes without special permission from the copyright holder, provided acknowledgement of the source is made. The United Nations Environment Programme would appreciate receiving a copy of any publication that uses this publication as a source. No use of this publication may be made for resale or for any other commercial purpose whatsoever without prior permission in writing from the United Nations Environment Programme. The United Nations Environment Programme promotes environmentally sound practices globally and in its own activities. This publication was printed on recycled paper, 100 per cent chlorine free. -
Radiation Risk in Perspective
PS010-1 RADIATION RISK IN PERSPECTIVE POSITION STATEMENT OF THE HEALTH HEALTH PHYSICS SOCIETY* PHYSICS SOCIETY Adopted: January 1996 Revised: August 2004 Contact: Richard J. Burk, Jr. Executive Secretary Health Physics Society Telephone: 703-790-1745 Fax: 703-790-2672 Email: [email protected] http://www.hps.org In accordance with current knowledge of radiation health risks, the Health Physics Society recommends against quantitative estimation of health risks below an individual dose of 5 rem1 in one year or a lifetime dose of 10 rem above that received from natural sources. Doses from natural background radiation in the United States average about 0.3 rem per year. A dose of 5 rem will be accumulated in the first 17 years of life and about 25 rem in a lifetime of 80 years. Estimation of health risk associated with radiation doses that are of similar magnitude as those received from natural sources should be strictly qualitative and encompass a range of hypothetical health outcomes, including the possibility of no adverse health effects at such low levels. There is substantial and convincing scientific evidence for health risks following high-dose exposures. However, below 5–10 rem (which includes occupational and environmental exposures), risks of health effects are either too small to be observed or are nonexistent. In part because of the insurmountable intrinsic and methodological difficulties in determining if the health effects that are demonstrated at high radiation doses are also present at low doses, current radiation protection standards and practices are based on the premise that any radiation dose, no matter how small, may result in detrimental health effects, such as cancer and hereditary genetic damage. -
Absorbed Dose in Radioactive Media Outline Introduction Radiation Equilibrium Charged-Particle Equilibrium Limiting Cases
Outline • General dose calculation considerations, Absorbed Dose in Radioactive absorbed fraction Media • Radioactive disintegration processes and associated dose deposition – Alpha disintegration Chapter 5 – Beta disintegration – Electron-capture transitions F.A. Attix, Introduction to Radiological – Internal conversion Physics and Radiation Dosimetry • Summary Introduction Radiation equilibrium • We are interested in calculating the absorbed dose in a. The atomic composition radioactive media, applicable to cases of of the medium is – Dose within a radioactive organ homogeneous – Dose in one organ due to radioactive source in another b. The density of the organ medium is • If conditions of CPE or RE are satisfied, dose homogeneous c. The radioactive source calculation is straightforward is uniformly distributed • Intermediate situation is more difficult but can be d. No external electric or handled at least in approximations magnetic fields are present Charged-particle equilibrium Limiting cases • Emitted radiation typically includes both • Each charged particle of a given type and photons (longer range) and charged energy leaving the volume is replaced by an particles (shorter range) identical particle of the same energy entering • Assume the conditions for RE are satisfied the volume • Consider two • Existence of RE is sufficient condition for CPE limited cases based • Even if RE does not exist CPE may still exist on the size of the (for a very large or a very small volume) radioactive object 1 Limiting cases: small object Limiting -
How Do Radioactive Materials Move Through the Environment to People?
5. How Do Radioactive Materials Move Through the Environment to People? aturally occurring radioactive materials Radionuclides can be removed from the air in Nare present in our environment and in several ways. Particles settle out of the our bodies. We are, therefore, continuously atmosphere if air currents cannot keep them exposed to radiation from radioactive atoms suspended. Rain or snow can also remove (radionuclides). Radionuclides released to them. the environment as a result of human When these particles are removed from the activities add to that exposure. atmosphere, they may land in water, on soil, or Radiation is energy emitted when a on the surfaces of living and non-living things. radionuclide decays. It can affect living tissue The particles may return to the atmosphere by only when the energy is absorbed in that resuspension, which occurs when wind or tissue. Radionuclides can be hazardous to some other natural or human activity living tissue when they are inside an organism generates clouds of dust containing radionu- where radiation released can be immediately clides. absorbed. They may also be hazardous when they are outside of the organism but close ➤ Water enough for some radiation to be absorbed by Radionuclides can come into contact with the tissue. water in several ways. They may be deposited Radionuclides move through the environ- from the air (as described above). They may ment and into the body through many also be released to the water from the ground different pathways. Understanding these through erosion, seepage, or human activities pathways makes it possible to take actions to such as mining or release of radioactive block or avoid exposure to radiation. -
Radionuclides (Including Radon, Radium and Uranium)
Radionuclides (including Radon, Radium and Uranium) Hazard Summary Uranium, radium, and radon are naturally occurring radionuclides found in the environment. No information is available on the acute (short-term) noncancer effects of the radionuclides in humans. Animal studies have reported inflammatory reactions in the nasal passages and kidney damage from acute inhalation exposure to uranium. Chronic (long-term) inhalation exposure to uranium and radon in humans has been linked to respiratory effects, such as chronic lung disease, while radium exposure has resulted in acute leukopenia, anemia, necrosis of the jaw, and other effects. Cancer is the major effect of concern from the radionuclides. Radium, via oral exposure, is known to cause bone, head, and nasal passage tumors in humans, and radon, via inhalation exposure, causes lung cancer in humans. Uranium may cause lung cancer and tumors of the lymphatic and hematopoietic tissues. EPA has not classified uranium, radon or radium for carcinogenicity. Please Note: The main sources of information for this fact sheet are EPA's Integrated Risk Information System (IRIS) (5), which contains information on oral chronic toxicity and the RfD for uranium, and the Agency for Toxic Substances and Disease Registry's (ATSDR's) Toxicological Profiles for Uranium, Radium, and Radon. (1) Uses Uranium is used in nuclear power plants and nuclear weapons. Very small amounts are used in photography for toning, in the leather and wood industries for stains and dyes, and in the silk and wood industries. (2) Radium is used as a radiation source for treating neoplastic diseases, as a radon source, in radiography of metals, and as a neutron source for research. -
Occupational Radiation Protection Record-Keeping and Reporting Guide
DOE G 441.1-11 (formerly G-10 CFR 835/H1) 05-20-99 OCCUPATIONAL RADIATION PROTECTION RECORD-KEEPING AND REPORTING GUIDE for use with Title 10, Code of Federal Regulations, Part 835, Occupational Radiation Protection Assistant Secretary for Environment, Safety and Health (THIS PAGE INTENTIONALLY LEFT BLANK) DOE G 441.1-11 i 05-20-99 CONTENTS CONTENTS PAGE 1. PURPOSE AND APPLICABILITY ........................................................ 1 2. DEFINITIONS ........................................................................ 2 3. DISCUSSION ........................................................................ 3 4. IMPLEMENTATION GUIDANCE ......................................................... 4 4.1 RECORDS TO BE GENERATED AND MAINTAINED ................................ 4 4.1.1 Individual Monitoring and Dose Records ........................................ 4 4.1.2 Monitoring and Workplace Records ............................................ 8 4.1.3 Administrative Records .................................................... 11 4.2 REPORTS ................................................................... 15 4.2.1 Reports to Individuals ...................................................... 16 4.2.2 Reports of Planned Special Exposures ......................................... 17 4.3 PRIVACY ACT CONSIDERATIONS .............................................. 17 4.3.1 Informing Individuals ...................................................... 17 4.3.2 Identifying Individuals ..................................................... 17 -
Development of Chemical Dosimeters Development Of
SUDANSUDAN ACADEMYAGADEMY OFOF SCIENCES(SAS)SGIENGES(SAS) ATOMICATOMIC ENERGYEhTERGYRESEARCHESRESEARCHES COORDINATIONCOORDII\rATI ON COUNCILCOUNCIL - Development of Chemical Dosimeters A dissertation Submitted in a partial Fulfillment of the Requirement forfbr Diploma Degree in Nuclear Science (Chemistry) By FareedFadl Alla MersaniMergani SupervisorDr K.S.Adam MurchMarch 2006 J - - - CONTENTS Subject Page -I - DedicationDedication........ ... ... ... ... ... ... ... ... ... ... ... ... ... ... ... ... ... ... ... I Acknowledgement ... '" ... ... ... ... ... ... '" ... ... ... ... '" ... '" ....... .. 11II Abstract ... ... ... '" ... ... ... '" ... ... ... ... -..... ... ... ... ... ... ..... III -I Ch-lch-1 DosimetryDosimefry - 1-1t-l IntroductionLntroduction . 1I - 1-2t-2 Principle of Dosimetry '" '" . 2 1-3l-3 DosimetryDosimefiySystems . 3J 1-3-1l-3-l primary standard dosimeters '" . 4 - 1-3-2l-3-Z Reference standard dosimeters ... .. " . 4 1-3-3L-3-3 Transfer standard dosimeters ... ... '" . 4 1-3-4t-3-4 Routine dosimeters . 5 1-4I-4 Measurement of absorbed dose . 6 1-5l-5 Calibration of DosimetryDosimetrvsystemsvstem '" . 6 1-6l-6 Transit dose effects . 8 Ch-2ch-2 Requirements of chemical dosimeters 2-12-l Introduction ... ... ... .............................................. 111l 2-2 Developing of chemical dosimeters ... ... .. ....... ... .. ..... 12t2 2-3 Classification of Dosimetry methods.methods .......................... 14l4 2-4 RequirementsRequiremsnts of ideal chemical dosimeters ,. ... 15 2-5 Types of chemical system . -
6.2.43A Radiation-Dominated Model of the Universe
6 BIG BANG COSMOLOGY – THE EVOLVING UNIVERSE 6.2.43A radiation-dominated model of the Universe R We have just seen that in the early Universe, the dominant energy density is that due to the radiation within the Universe. The Friedmann equation that was described in Chapter 5 (Box 5.4) can be solved for such conditions and the way in which the scale factor varies with time for such a model is shown in Figure 6.7. One important feature of such a model is that the scale factor varies in the following way: R(t) ∝ t1/2 (6.17) 0 t −4 Because the energy density of radiation is dominant for times when R(t)/R(t0) < 10 , all cosmological models which start at t = 0 with R(0) = 0, will go through a phase Figure 6.73The evolution of the that is well described by this radiation-dominated model. Thus we are in the rather scale factor with time in a remarkable position that regardless of which type of cosmological model best cosmological model in which the dominant contribution to the describes the Universe at the present, we can be reasonably confident that we energy density arises from the know how the scale factor varied with time in the first few tens of thousands of radiation within the Universe years of the big bang. (i.e. during the radiation-dominated However, the temperature of the background radiation varies with scale factor era). according to T(t) ∝ 1/R(t) (Equation 6.6). It follows that during the radiation- dominated era the temperature of the background radiation varies with time according to T(t) ∝ t −1/2 (6.18) This describes how temperature changes with time in an expanding universe where the energy density of radiation is the dominant component. -
The International Commission on Radiological Protection: Historical Overview
Topical report The International Commission on Radiological Protection: Historical overview The ICRP is revising its basic recommendations by Dr H. Smith Within a few weeks of Roentgen's discovery of gamma rays; 1.5 roentgen per working week for radia- X-rays, the potential of the technique for diagnosing tion, affecting only superficial tissues; and 0.03 roentgen fractures became apparent, but acute adverse effects per working week for neutrons. (such as hair loss, erythema, and dermatitis) made hospital personnel aware of the need to avoid over- Recommendations in the 1950s exposure. Similar undesirable acute effects were By then, it was accepted that the roentgen was reported shortly after the discovery of radium and its inappropriate as a measure of exposure. In 1953, the medical applications. Notwithstanding these observa- ICRU recommended that limits of exposure should be tions, protection of staff exposed to X-rays and gamma based on consideration of the energy absorbed in tissues rays from radium was poorly co-ordinated. and introduced the rad (radiation absorbed dose) as a The British X-ray and Radium Protection Committee unit of absorbed dose (that is, energy imparted by radia- and the American Roentgen Ray Society proposed tion to a unit mass of tissue). In 1954, the ICRP general radiation protection recommendations in the introduced the rem (roentgen equivalent man) as a unit early 1920s. In 1925, at the First International Congress of absorbed dose weighted for the way different types of of Radiology, the need for quantifying exposure was radiation distribute energy in tissue (called the dose recognized. As a result, in 1928 the roentgen was equivalent in 1966). -
Rapport Du Groupe De Travail N° 9 Du European Radiation Dosimetry Group (EURADOS) – Coordinated Network for Radiation Dosimetry (CONRAD – Contrat CE Fp6-12684)»
- Rapport CEA-R-6220 - CEA Saclay Direction de la Recherche Technologique Laboratoire d’Intégration des Systèmes et des Technologies Département des Technologies du Capteur et du Signal Laboratoire National Henri Becquerel RADIATION PROTECTION DOSIMETRY IN MEDECINE REPORT OF THE WORKING GROUP N° 9 OF THE EUROPEAN RADIATION DOSIMETRY GROUP (EURADOS) COORDINATED NETWORK FOR RADIATION DOSIMETRY (CONRAD – CONTRACT EC N° FP6-12684) - Juin 2009 - RAPPORT CEA-R-6220 – «Dosimétrie pour la radioprotection en milieu médical – Rapport du groupe de travail n° 9 du European Radiation Dosimetry group (EURADOS) – Coordinated Network for Radiation Dosimetry (CONRAD – contrat CE fp6-12684)» Résumé - Ce rapport présente les résultats obtenus dans le cadre des travaux du WP7 (dosimétrie en radioprotection du personnel médical) de l’action coordonnée CONRAD (Coordinated Network for Radiation Dosimetry) subventionné par la 6ème FP de la communauté européenne. Ce projet a été coordonné par EURADOS (European RadiationPortection group). EURADOS est une organisation fondée en 1981 pour promouvoir la compréhension scientifique et le développement des techniques de la dosimétrie des rayonnements ionisant dans les domaines de la radioprotection, de la radiobiologie, de la thérapie radiologique et du diagnostic médical ; cela en encourageant la collaboration entre les laboratoires européens. Le WP7 de CONRAD coordonne et favorise la recherche européenne pour l'évaluation des expositions professionnelles du personnel sur les lieux de travail de radiologie thérapeutique et diagnostique. La recherche est organisée en sous-groupes couvrant trois domaines spécifiques : 1. Dosimétrie d'extrémité en radiologie interventionnelle et médecine nucléaire : ce sous- groupe coordonne des investigations dans les domaines spécifiques des hôpitaux et des études de répartition des doses dans différentes parties des mains, des bras, des jambes et des pieds ; 2. -
PE1128 Radiation Exposure in Medical Imaging
Radiation Exposure in Medical Imaging This handout answers questions about radiation exposure and what Seattle Children’s Hospital is doing to keep your child safe. Medical imaging uses machines and techniques to provide valuable information about your child’s health. It plays an important role in helping your doctor make the correct diagnosis. Some of these machines use radiation to get these images. We are all exposed to small amounts of radiation in normal daily life from soil, rocks, air, water and even some of the foods we eat. This is called background radiation. The amount of background radiation that you are exposed to depends on where you live and varies throughout the country. The average person in the United States receives about 3 milli-Sieverts (mSv) per year from background radiation. A mSv is a unit of measurement for radiation, like an inch is a unit of length. Which medical MRI and ultrasound do not use ionizing (high-energy) radiation to make imaging exams images. MRI uses magnets and radio waves, and ultrasound uses sound waves. use radiation? Diagnostic An X-ray is a form of energy that can pass through your child’s bones and Radiography tissues to create an image. The image created is called a radiograph, sometimes referred to as an “X-ray.” X-rays are used to detect and diagnose conditions in the body. CT scan A CT (computed tomography) scan, sometimes called a “CAT scan,” uses X-rays, special equipment, and computers to make pictures that provide a multidimensional view of a body part. -
Pediatric Considerations Before, During, and After Radiological Or Nuclear Emergencies
TECHNICAL REPORT Pediatric Considerations Before, During,Martha S. Linet, MD, MPH, and a, b Ziad Kazzi, After MD, c, d Jerome A. RadiologicalPaulson, MD, FAAP, e COUNCIL ON ENVIRONMENTAL HEALTH or Nuclear Emergencies Infants, children, and adolescents can be exposed unexpectedly to ionizing abstract radiation from nuclear power plant events, improvised nuclear or radiologic dispersal device explosions, or inappropriate disposal of radiotherapy equipment. Children are likely to experience higher external and internal radiation exposure levels than adults because of their smaller body and aRadiation Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, Bethesda, Maryland; bAgency for organ size and other physiologic characteristics as well as their tendency to Toxic Substances and Disease Registry, Centers for Disease Control pick up contaminated items and consume contaminated milk or foodstuffs. and Prevention, Atlanta, Georgia; cNational Center for Environmental Health, Centers for Disease Control and Prevention, Atlanta, Georgia; This technical report accompanies the revision of the 2003 American dDepartment of Emergency Medicine, Emory University, Atlanta, Georgia; and eDepartment of Pediatrics, School of Medicine and Health Academy of Pediatrics policy statement on pediatric radiation emergencies Sciences, and Department of Environmental and Occupational Health, by summarizing newer scientific data from studies of the Chernobyl and the Milken Institute School of Public Health, George Washington University, Washington, District of Columbia Fukushima Daiichi nuclear power plant events, use of improvised radiologic Drs Linet and Kazzi contributed much of the technical information in dispersal devices, exposures from inappropriate disposal of radiotherapy this report, and Dr Paulson was responsible for drafting the document; equipment, and potential health effects from residential proximity to and all authors approved the final manuscript as submitted.