Prepared by numerous specialists
E. P. Blizard t, A. B. Chilton,
M. Grotenhuis, A. Honig, Th. A. Jaeger
H. H. Eisenlohr Coordinating Editor
Sponsored by International Atomic Energy Agency Vienna
Volume I Shielding Fundamentals and Methods
Springer-Verlag Berlin Heidelberg GmbH 1968
With 467 Figures
ISBN 978-3-662-23757-1 ISBN 978-3-662-25858-3 (eBook) DOI
10.1007/978-3-662-25858-3
All rights reserved No part of this book may be translated or
reproduced in
any form without written permission from Springer-Verlag Berlin
Heidelberg GmbH 1968
© Springer-Verlag Berlin Heidelberg 1968 Originally published by
Springer-Verlag Berlin • Heidelberg in 1968
Softcover reprint of the hardcover 1st edition 1968
Library of Congress Catalog Card Number 68-19816
The use of general descriptive names, trade names, trade marks,
etc. in this publicationevenifthe former are not especially
identified, is not to be taken as a sign that such names, as
understood by the Trade
Marks and Merchandise Marks Act, may accordingly be used by
anyone
Title-No, 1416
Prepared by numerous specialists
E. P. Blizard t, A. B. Chilton,
M. Grotenhuis, A. Honig, Th. A. Jaeger
H. H. Eisenlohr Coordinating Editor
Sponsored b International Atomic Energy Agency Vienna
Volume I Shielding Fundamentals and Methods
Springer-Verlag Berlin Heidelberg GmbH 1968
With 467 Figures
ISBN 978-3-662-23757-1 ISBN 978-3-662-25858-3 (eBook) DOl
10.1007/978-3-662-25858-3
All rights reserved No part of this book may be translated or
reproduced in
any form without written permission from Springer-Verlag Berlin
Heidelberg GmbH 1968
©Springer-Verlag Berlin Heidelberg 1968 Originally published by
Springer-Verlag Berlin • Heidelberg in 1968
Softcover reprint of the hardcover 1st edition 1968
Library of Congress Catalog Card Number 68-19816
The use of general descriptive names, trade names, trade marks,
etc. in this publicationevenifthe former are not especially
identified, is not to be taken as a sign that such names, as
understood by the Trade
Marks and Merchandise Marks Act, may accordingly be used by
anyone
Title-No, 1416
IN MEMORIAM
1916-1966
EvERITT P. BLIZARD has had a greater effect on the development of
the science and technology of radiation shielding than any other
single person. Almost from the inception of the nuclear programs
for peaceful purposes, he assumed a position of leadership in the
field of radiation shielding which he never relinquished until his
death. Although his activities have been centered on the research
programs of his own coun try. the United States, thrOugh his
participation in numerous international conferences he has also had
a major effect on the programs of other countries. Radiation
shielding of all types, throughout the world, has thus felt his
touch as experimenter, teacher, administrator, editor, and
advisor.
It was inconceivable that a comprehensive shielding handbook could
have been started without his advice and collaboration, and EvERITT
P. BLIZARD -in spite of his many other duties- generously agreed to
serve as one of the editors. The first intima tion of his last
illness came within two years afterwards, and it is characteristic
of him that he tried for some months to continue work on Compendium
manuscripts after his failing strength forced him to give up all
his other duties at the Oak Ridge National Laboratory.
By his death, the editors have lost a close friend and an inspiring
collaborator; the shielding profession has lost a great leader; and
the world has lost an outstanding citizen.
List of Editors and Contributors Editors
jAEGER, R. G. Universitat Mainz, Institut fiir Klinische
Strahlenkunde, 65 Mainz, F.R.G.; formerly member of
Physikalisch-Technische Bundesanstalt, Braunschweig, and Senior
Officer in the International Atomic Energy Agency, Vienna, Division
of Isotopes.- Chapter 1, Sections 2.1., 2.2.
BLIZARD t. E. P. Formerly Oak Ridge National Laboratory, Oak Ridge,
Tennessee 37 830, U.S.A.
CHILTON, A. B.
207 Nuclear Engineering Laboratory, University of Illinois, Urbana,
Illinois 61 801, U.S.A. Chapters 4, 8
GROTENHUIS, M. Argonne National Laboratory, 9700 South Cass Avenue,
Argonne, Illinois 60439, U.S.A. Section 2.J., Chapters J, 5
HoNIG, A.
Brno Technical University, Hlinky 48, Brno, C.S.S.R.- Chapter
9
JAEGER, TH. A. Bundesanstalt fiir Materialpriifung, Abteilung
Bauwesen, 1 Berlin 45, F. R. G.; (Technische Univer sitat Berlin,
Fakultat fiir Bauingenieurwesen, 1 Berlin 12). - Chapters 6, 7,
10
EISENLOHR, H. H.
Contributors to Volume I AALTO, E.
Imatran Voima Osakeyhti6, Box 10 138, Helsinki 10, Finland.
-Sections 8.2.3., 8.2.7.
ALTER, J. Israel Atomic Energy Commission, Nuclear Research
Centre-Negev., P.O. Box 9001, Beer Sheva, Israel. Section
6.8.
ARNOLD, E. D. Chemical Technology Division, Oak Ridge National
Laboratory, P.O. Box X, Oak Ridge, Tennessee 37 830, U.S.A.-
Sections 2.1.2, 2.3.1.1.
ARONSON, R. New York University, University Heights, New York, N.Y.
10 453, U.S.A. -Section 3.3.2.
AVERY, A. F. Winfrith Shielding Group, Building 51 OT, Atomic
Energy Research Establishment, Harwell, Didcot, Berkshire, U.K.
-Section 5.2.2.2.
BERGELSON, B. R. Institute of Theoretical and Experimental Physics,
Moscow M-259, U.S.S.R.- Sections 8.2.1., 8.2.2.
BERGER, M. J. National Bureau of Standards, Washington, D. C. 20
234, U.S.A. -Sections 4.1 .. 4.2.
BIRO, G. G. Gibbs & Hill Inc., Consulting Engineers, 393
Seventh Avenue, New York, N.Y. 10 001, U.S.A. Section 3.1.
BLIZARD f, E. P. Formerly Oak Ridge National Laboratory, Oak Ridge,
Tennessee 37 830 U.S.A. -Sections 6.1., 6 7.
BONILLA, C. F. School of Engineering and Applied Science, Columbia
University, 520 West 120th Street, New York, N.Y. 10 027, U.S.A.-
Sections 7.4.1.-7.4.5.
BRODER, D. L. Institute of Physics and Power Engineering, Obninsk,
U.S.S.R. -Section 5.J.
VI List of editors and contributors
BRYAN, Jr., F. A. Research Triangle Institute, Box 12 194, Research
Triangle Park, North Carolina 27 709, U.S.A. Section 4.3.1.3.
BuNEMANN, D. Gesellschaft fiir Kernenergieverwertung in Schiffbau
und Schiffahrt m.b.H., Institut fiir Reaktor physik, 2057
Geesthacht-Tesperhude, F.R.G.- Section 4.3.2.
BURRILL, E. A. High Voltage Engineering Corporation, 703 Welch
Road, Suite F-I, Palo Alto, California 94 304, U.S.A.- Sections
2.2.1.1., 2.2.1.2.
BURRUS, W. R. Oak Ridge National Laboratory. Present address:
Tennecomp, Inc., Box J, Oak Ridge, Tennessee 37 830, U.S.A.-
Sections 8.1.6., 8.1.7., 8.2.6.
BuTLER, J. Winfrith Shielding Group, Building 51 OT, Atomic Energy
Research Establishment, Harwell, Didcot, Berkshire, U.K. -Section
5.2.2.2.
CHILTON, A. B.
207 Nuclear Engineering Laboratory, University of Illinois, Urbana,
Illinois 61 801, U.S.A. Sections 4.3.1.1., 4.3.1.2.
CLAIBORNE, H. c. Oak Ridge National Laboratory, P.O. Box X, Oak
Ridge, Tennessee 37 830, U.S.A. Sections 7.1., 7.3., 8.2.5.
CLARKE, E. T. Technical Operations, Inc., Burlington, Massachusetts
02 103, U.S.A.- Section 4.5.3.
CLIFFORD, C. E.
CLIFFORD, c. E.
Oak Ridge National Laboratory, P.O. Box X, Oak Ridge, Tennessee 37
830, U.S.A.- Section 8.2.5.
EGoRov, Yu. A. Atomic Energy Institute, Kurchatov, Moscow, U.S.S.R.
-Section 5.2.1.2.
FoDERARo, A. Nuclear Engineering Department, The Pennsylvania State
University, 231 Sackett Building, Uni versity Park, Pennsylvania
16 802, U.S.A.- Sections 3.2., 6.1.-6.6., 6.8., 7.2.
FRENCH, R. L. Radiation Research Associates, Inc., 1506 West
Terrell Avenue, Fort Worth, Texas 76 104, U.S.A. Section
5.4.2.
GoussEv, N. G. Institute of Biophysics (The Ministry of Public
Health of u.S.S.R.), Lhivopisnaya 22, Moscow D-182, U.S.S.R.-
Sections 1.3., 6.1., 6.4., 6.5., 6.6.5.-6.6.8.
GRONROOS, H. California Institute of Technology, Jet Propulsion
Laboratory, 4800 Oak Grove Drive, Pasadena, California 91103,
U.S.A. -Section 5.2.3.2.
GROTENHUIS, M. Argonne National Laboratory, 9700 South Cass Avenue,
Argonne, Illinois 60 439, U.S.A. Sections 2.3.2.1., 2.3.2.4.
HoovER, L. J. Nuclear Engineering DepaTtment, The Pennsylvania
State University, 231 Sackett Building, Uni versity Park,
Pennsylvania 16 802, U.S.A.- Section 7.2.
HuBBELL, J. H.
National Bureau of Standards, Washington, D. C. 20 234, U.S.A.-
Sections 4.1., 4.2.
HUDDLESTON, c. M. U.S. Naval Radiological Defense Laboratory, San
Francisco, California 94 135, U.S.A. Sections 8.1.1- 8.1.5.
KEEPIN, G. R. Los Alamos Scientific Laboratory, University of
California, P.O. Box 1663, Los Alamos, New Mexico 87 544, U.S.A.-
Section 2.3.1.2.
List of editors and contributors
KovALEV, E. E. The Ministry Public Health of U.S.S.R., Rachmanovsky
3, Moscow, U.S.S.R. Sections 6.1.-6.3., 6.6.1.-6.6.4.
KRUMBEIN, A. D.
United Nuclear Corporation, Research and Engineering Center,
Grasslands Road, Elmsford, New York 10 523, U.S.A.- Section
3.3.1.
KUKHTEVICH, V. I. Institute of Physics and Power Engineering,
Obninsk, U.S.S.R.- Sections 5.2.3.1., 5.4.1.2.
LAFORE, P. Commissariat a l'Energie Atomique, Centre d'Etudes
Nuc!eaires de Fontenay-aux-Roses, Fontenay aux-Roses, Seine,
France.- Section 5.2.1.1.
LEDoux, ] . C. Nuclear Division, Flow Corporation, 6060 Duke
Street-Suite 101, Alexandria, Virginia 22 302, U.S.A. Sections
8.1.1.-8.1.5.
LEIMDORFER, M .. Industri-Matematik AB, De Geersgatan 8, Stockholm
NO, Sweden.- Sections 4.4., 5.4.1.1.
1\'IADEY, RICHARD
Physics Department, Clarkson College of Technology, Potsdam, New
York 13 676, U.S.A. Section 2. 2. 2. 1.
MAERKER, R. E. Oak Ridge National Laboratory, P.O. Box X, Oak
Ridge, Tennessee 37 830, U.S.A.- Section 8.2.5.
MAIENSCHEIN, F. C. Oak Ridge National Laboratory, P.O. Box X, Oak
Ridge, Tennessee 37 830, U.S.A. Sections 2.3.1.3., 2.3.1.4.
MARABLE, J. H. Oak Ridge National Laboratory, P.O. Box X, Oak
Ridge, Tennessee 37 830, U.S.A.- Section 7.2.
MASHKOVICH, v. P. Moscow Engineering Physical Institute, Moscow
M-409, U.S.S.R.- Sections 8.2.1., 8.2.2.
McARTHY, A. E. Argonne National Laboratory, 9700 South Cass Avenue,
Argonne, Illinois 60 439, U.S.A. Section 2.3.2.4.
MEHL, ]. G. International Atomic Energy Agency, Karntnerring,
Vienna, Austria. Present address: Gesellschaft fiir Kernforschung
m.b.H., Postfach 947, 75 Karlsruhe, F.R.G. -Section 1.2.
MITTELMAN, P. s. MAGI (Mathematical Applications Group, Inc.), 180
South Broadway, White Plains, New York 10 605, U.S.A. -Section
3.3.3.
MORGAN, I. L. Texas Nuclear Corporation, P.O. Box 9267-Allandale
Station, Austin, Texas 78 756, U.S.A. Section 2.3.2.2.
MYNATT, F. R. Computing Technology Center, Union Carbide
Corporation, Nuclear Division, P.O. Box P, Oak Ridge, Tennessee 37
830, U.S.A.- Section 3.3.4.
NETECHA, M. E. Atomic Energy Institute, Kurchatov, Moscow,
U.S.S.R.- Section 5.2.1.2.
NILSSON, ]. The Axel Johnson Institute for Industrial Research,
Nynashamn, Sweden.- Section 8.2.4.1.
O'REILLY, B. D. Atomics International, A Division of North
American-Rockwell Corporation, 8900 De Soto Avenue, Canoga Park,
California 91 304, U.S.A.- Section 3.3.1.
PREISER, S. Polytechnic Institute of Brooklyn, 333 Jay Street,
Brooklyn, New York 11 201, U.S.A. Section 3.3.3.
RICHTER, G. Gesellschaft fiir Kernenergieverwertung in Schiffbau
und Schiffahrt m.b.H., Institut fiir Reaktor physik, 2057
Geesthacht-Tesperhude, F.R.G. -Section 4.3.2.
VIII List of editors and contributors
Rossr, H. H. Radiological Research Laboratory, Department of
Radiology, College of Physicians and Surgeons, Columbia University,
630 West 168th Street, New York, N.Y. 10 032, U.S.A. -Section
1.1.
SANDLIN, R. Saab Aktiebolag, Linkiiping, Sweden- Sections 8.2.4.1.,
8.2.7.
ScHAEFFER, N. M. Radiation Research Associates, Inc., 1506 West
Terrell Avenue, Fort Worth, Texas 76 104, U.S.A. Section
4.5.2.
SELPH, w. Radiation Research Associates, Inc., 1506 West Terrell
Avenue, Fort Worth, Texas 76 104, U.S.A. Section 5. 1.
SONNEMANN, G. 30 Hurdle Fence Drive, Avon, Connecticut 06 001,
U.S.A. -Sections 7.4.6., 7.5.
SuscHNY, 0. International Atomic Energy Agency, Kii.rntnerring,
Vienna, Anstria.- Section 2.1.1.
THOMAS, R. H. Stanford University, Health Physics and Occupational
Health, 67 Encina Hall, Stanford, California 94 305, U.S.A. -
Section 2.2.2.2.
TRUBEY, D. K. Radiation Shielding Information Center, Oak Ridge
National Laboratory, P.O. Box X, Oak Ridge, Tennessee 37 830,
U.S.A. -Sections 2.3.2.3., 5.2.2.1.
TsYPIN, S. G. Institute of Physics and Power Engineering, Obninsk,
U.S.S.R.- Sections 5.2.3.1., 5.3.
VESELKIN, A. P. Atomic Energy Institute, Kurchatov, Moscow,
U.S.S.R.- Section 5.2.1.2.
VESELY, w. E. 201 Nuclear Engineering Laboratory, University of
Illinois, Urbana, Illinois 61 801, U.S.A. Sections 8.2.4.2.,
8.3.
WELLS, M. B. Radiation Research Associates, Inc., 1506 West Terrell
Avenue, Fort Worth, Texas 76 104, U.S.A. Section 5. 4.2.
WIDERDE, R. Swiss Federal Institute of Technology, Ziirich,
Switzerland. -Sections 2.2.1.3., 2.2.1.4.
WYCKOFF, H. 0. Armed Forces Radiobiology Research Institute,
Defense Atomic Support Agency, Bethesda, Maryland 20 014, U.S.A.-
Section 1.1.
YARMUSH, D. L. Courant Institute of Mathematical Sciences, New York
University, 251 Mercer Street, New York, N.Y. 10 012, U.S.A.-
Section 3.3.2.
Preface
The need has arisen for a comprehensive handbook for engineers
faced with problems of radiation shielding design. Although there
are several excellent books on shielding, they either do not give
enough consideration to the many practical design problems, or are
limited to special aspects of the subject.
Recognizing the universal need, the International Atomic Energy
Agency decided to sponsor the publication ofthe present Engineering
Compendium on Radiation Shield ing. At the first editorial
discussions it was agreed that, if such a book were to be
undertaken, it would be appropriate not only to create a useful
design tool for the practising engineer but also to include
well-referenced basic data for the research worker. Although trying
to keep the book down to a reasonable size, the editors have aimed
at a complete presentation of the subject, covering and linking
both the tech nology and the science of shielding.
Efforts to make terms and definitions consistent throughout have
been only partially successful, owing to the continuing development
of new ideas. However, inconsisten cies that could not be
eliminated are identified whenever possible.
The Engineering Compendium on Radiation Shielding is arranged as
follows: Vol. I, "Shielding Fundamentals and Methods", explains
basic concepts, gives fundamental data, and describes analytical
methods; it also contains data and formulae of an applied nature.
Vol. II, "Shielding Materials and Design", deals fully with the
prop erties of shielding materials and with the practical design
problems associated with gamma and neutron radiations in
industrial, scientific and medical applications of atomic energy.
Typical numerical examples are given to illustrate shield analysis.
The editors hope that with this arrangement the handbook will
completely fulfil the need of all those engaged in radiation
shielding, and also believe that it will be useful in teaching at
colleges and universities.
Dr. E. P. BLIZARD is named as an editor because of his great
efforts in getting the Compendium started. His untimely death
denied us his valuable help in the later editorial work.
The participation and contributions of three of the divisions of
the International Atomic Energy Agency, the Division of Life
Sciences (formerly the Division of Iso topes), the Division of
Nuclear Power and Reactors, and the Division of Health and Safety
are gratefully acknowledged. These divisions were represented by
Messrs. H. H. EISENLOHR, A. MERTON and J. G. MEHL. Valuable work by
the translation staff of the IAEA is also greatly
appreciated.
The Board of Editors are also grateful to the United States Atomic
Energy Com mission for financially supporting their
meetings.
The editors have been particularly pleased by the close
co-operation that has existed between them and the representatives
of Springer-Verlag, who were always willing to meet the exacting
demands made on them, many of which were beyond normal publishing
requirements.
July 1968 The Editors
1. 2. Irradiation limits
1.3. Relationship between dose equivalent (absorbed dose) and
fluence (flux density)
Chapter 2
Radiation Sources
2.2. Particle accelerators 0
2. 2.1. Electron accelerators 2.2.1.1. X-ray generators 2.2.1.20
Van de Graaff and other direct electron accelerators . 2.2.1.3.
Betatrons and synchrotrons. . . . o . 2.2.1.4. Linear electron
accelerators ("Linacs")
2.2.2. Nucleon accelerators 0 . 0 . . . 0 0 . 2.2.2.1. Nucleon
accelerators in general . 2. 2. 2. 2. Proton synchrotron
accelerators
2.3. Nuclear reactors . . o . o o o o o o
2. 3.1. Radiation from nuclear fission 0 2.3.1.1. Prompt fission
neutrons 2.3.1.2. Delayed fission neutrons 2.3.1.3. Prompt-fission
ga=a rays. 2.3.J.4. Fission-product gamma rays
2.3.2. Radiation from secondary interactions 2.3.2.1. Capture gamma
rays 2.3.2.2. Gamma rays from inelastic neutron scattering 2.3.2.3.
Photoneutrons . . . . 2o3.2.4. Activation gamma rays o o . o . 0 .
. . .
Chapter 3
3.1. Application of the Monte Carlo method to shielding 0
3.2. Point kernel methods.
3.3o Transport method o o
3.3.1o Neutron attenuation in hydrogenous media by the method of
moments
3.302. Matrix methods . . o o o o o 0
3.3.3o Direct integration methods (Niobe)
3.3.4. The discrete ordinates method (Sn)
6
12
20
20
30
36
49 49 56
101
124
127
4. 2. Photon atomic cross sections.
4.3. Broad beam attenuation . .
4. 3.1. Homogenous mixtures 4. 3.1.1. General . . . 4.3.1.2.
Buildup factor 4.3.1.3. Differential energy spectra
4. 3. 2. Multilayered shields
4.4. The backscattering of photons .
4.5. Air scattering . . . . . . . .
4.5.2. Energy and angle distributions in air for gamma rays .
4.5.3. Photon fields near earth-air interface . . . . . ...
5.1. Interaction processes . . . . . .
5.2 Attenuation in hydrogenous media (Methods and results)
261
5.2.1. Diffusion and age diffusion methods 261 5.2.1.1. Two-group
method . . 261 5.2.1.2. Multi-group method . . . . 264
5.2.2. Removal-diffusion combination 270 5.2.2.1. Combination
diffusion methods 270 5.2.2.2. Removal-diffusion theory. . .
273
5.2.3. Removal theory . . . . . . . . . . 301 5.2.3.1. Removal
cross-section method of neutron penetration 301 5.2.3.2. Energy
dependent removal cross-sections in fast neutron shielding theory
305
5.3. Attenuation in non-hydrogenous media 322
5.4. Neutron scattering . . . . . . . . . 330
5.4.1. The backscattering of neutrons 330 5.4.1.1. Theory . . . . .
. 330 5.4.1.2. Example . . . . . . 346
5. 4. 2. The air-scattering of neutrons 350
Chapter 6
6.1. Point and extended sources
6.2. Line sources . .
6.6. Derivation of formulae . . .
6. 7. Geometrical transformations .
363
367
368
374
387
393
403
411
7. 2. Heat generation by neutrons. . . . . . . . . . . .
7.3. Analytical solutions for heat generation distributions in
regular geometric~
7.4. Temperature distribution in radiation shields
7.4.1. Introduction . . . . . . . . .
7.4.3. Heat conduction within shields: Discussion of principles aud
simplified methods of analysis .......... .
417
438
441
450
450
450
453
7.4.5. Techniques for the solution of complex thermal problems . .
. . . . . . . . . . . 460
7.4.6. Solution of the nondimensionalized heat conduction equation
by the usc of finite integral transform techniques . . . . . . . .
. . . . . . 462
7.5. Radiation induced thermal stresses in long hollow cylinders .
. . . . . . . 473
Chapter 8
8. 1.1. General comments . .
8.1.2. Straight cylindrical duct.
8.1. 5. Rectangular ducts with more than one right-angle bend
8.1.6. Random voids and lumps
8.1. 7. Regular geometric void shapes
8.2. Attenuation of neutrons
8.2.1. Empty cylindrical ducts
8.2.2. Straight cylindrical ducts, filled with material differing
from shield material
8.2.3. Liquid filled cylindrical ducts
8.2.4. Annular (cylindrical) ducts. 8.2.4.1. Straight ducts
8.2.4.2. Stepped ducts
8.2.5. Neutron attenuation in rectangular ducts
8.2.6. Voids in neutron shields ....... .
8.2. 7. Fast neutron dose in a material surrounding a cylindrical
duct
8.3. Neutron streaming .
Chapter 9: Nuclear, Physical and Mechanical Properties and
Technology of Shielding Materials
Chapter 10: Shield Design and Engineering
487
487
487
488
488
489
490
495
497
497
508
512
by H. 0. 'WYCKOFF and H. H. Rossi
1.1.1. INTRODUCTION The quantities and units useful in radiation
shield
ing have been considered on an international scale by the
International Commission on Radiological Units and Measurements
(ICRU) since 1928, when the roentgen was specified as a unit of
what was then termed the "X-ray intensity" [I]. In 1953 the same
organization defined the quantity "absorbed dose" applicable to any
radiation and recommended that its (special) unit be the rad (equal
to 100 ergs/g) [2]. More recent consideration of radiation quan
tities and units by the Commission culminated in a report on the
subject in 1962 [3]. Most national and other international
organizations are accepting these definitions of the ICRU. The 1962
ICRU report is, therefore, a primary reference for this section of
the Compendium. Direct quotations from this report and the 1963
Report of the ICRP-ICRU RBE-Committee [ 4] will appear in sans
serif type in this chapter. In some instances these definitions
will be followed by brief comments.
As used here the term "quantity" denotes a phy sical entity used
for the precise description of a phenomenon and defined so as to be
measurable [5]. A unit is a particular sample of a quantity of such
magnitude that it is assigned the measure "1". Samples of different
magnitude are then expressed by the product of their measure and
the unit. A common unit is one 'vhich is the product or quotient of
the fundamental units. Occasionally a unit has a special name and
is associated with a particular quantity. Such units are called
special units.
Thus, according to the above definition, the quantity specifies the
type of phenomenon under consideration and the measure and unit
indicate the magnitude. It is obvious that~except for special
units-a unit by itself conveys no information regarding the type of
phenomenon under conside ration.
The 1962 ICRU report also contains definitions of general terms
that do not denote quantities in the sense referred to above:
Directly ionizing particles are charged particles ( elec trons,
protons, <X- particles, etc.) having sufficient kinetic energy
to produce ionization by collision.
1 Engineering Compendium, Vol. I
Indirectly ionizing particles are uncharged particles (neutrons,
photons, etc.) which can liberate directly ionizing particles or
can initiate a nuclear transformation.
Ionizing radiation is any radiation consisting of di rectly or
indirectly ionizing particles or a mixture of both.
Comment: It is true that an indirectly ionizing par ticle produces
an ion in the act of liberating a directly ionizing particle. For
example the first step in the photo electric effect is that a
photon ejects a high speed elec tron from an atom which then
becomes a positive ion. Such a photon is nevertheless not
considered as directly ionizing radiation since it is not a charged
particle as required by the definition above.
A nuclide is a species of atom having specified num bers of
neutrons and protons in its nucleus.
Comment: Some authors wish to distinguish between nuclear isomers
by the addition of "and given nuclear energy state". However, this
formulation has not vet been generally adopted. According to the
definition given here, nuclear isomers constitute the same
nuclide.
The energy imparted by ionizing radiation to the matter in a volume
is the difference between the sum of the energies of all the
directly and indirectly ionizing particles which have entered the
volume and the sum of the energies of all those which have left it,
minus the energy equivalent of any increase in rest mass that took
place in nuclear or elementary particle reactions within the
volume.
Notes: (a) The above definition is intended to be exactly
equivalent to the previous meanings given by the ICRU to "energy
retained by matter and made locally available" or "energy which
appears as ionization, excitation, or changes of chemical bond
energies". The present formulation specifies what energy is to be
in cluded without requiring a lengthy, and possibly in complete,
catalogue of the different types of energy transfer.
(b) Ultimately, most of the energy imparted will be degraded and
appear as heat. Some of it, however, may appear as a change in
interatomic bond energies. More over, during the degradation
process the energy will diffuse and the distribution of heat
produced may be different from the distribution of imparted energy.
For
2 1. Dosimetric fundamentals and irradiation limits [Ref. p.
5
these reasons the energy imparted cannot always be equated with the
heat produced.
(c) The quantity energy imparted to matter in a given volume is
identical with the quantity often called integral absorbed dose in
that volume.
Comment: This definition is provided as a basis for the definition
of absorbed dose (see below).
Three general types of quantities are of interest for radiation
shielding. These are material radiation quantities, physical
radiation quantities and bio physical radiation quantities.
The first two types must be distinguished because of the
statistical nature of radiation and its inter actions. The
material quantities are those that for a given type and energy of
radiation are functions of the material only-regardless of the
amount of radiation received or the rate at which it is deliver
ed. Consequently in a determination of their magnitude a sufficient
number of interactions can be observed to assure that an
unambiguous numeri cal value is obtained; that is, one with an
insigni ficant statistical uncertainty. Hence the quotients of
these quantities may be expressed as ordinary differential
quotients (see Sec. 1.1.2.).
However, for quantities that are proportional to the amount of
radiation received or the rate at which it is delivered, the number
of interactions in a specific mass or time may be so small that
sta tistical considerations enter. Thus the energy ab sorbed in a
given small mass may be different from that in an adjacent equal
mass and an unambiguous quotient of absorbed energy by mass can
then be deduced only from an averaging process or as a result of
repeated experimental determinations. The symbol Ll is employed in
the definition of the quantities that may be concerned in such
averaging procedures. All such quantities are listed in the section
entitled "Physical Radiation Quantities"' (see Sec. 1.1.3.).
The third type of quantity considered here, the biophysical
quantity, depends not only on physical considerations, but also on
biological factors of importance in radiation protection. These
quanti ties are considered in Sec. 1.1. 4.
1.1.2. MATERIAL RADIATION QUANTITffiS
The mass attenuation coefficient (p/~) of a material for indirectly
ionizing particles is the quotient of dN by the product of ~. N,
and dl where N is the number of particles incident normally upon a
layer of thickness dl and density ~. and d N is the number of
particles that experience interactions in this layer.
(1.1.-1)
Notes: (a) The term "interactions" refers to processes whereby the
energy or direction of the indirectly ionizing particles is
altered.
(b) For X- or gamma radiations
f.lTGGcohX -=-+-+--+-. ~ ~ ~ ~ ~
(1.1.-2)
where •I ~ is the mass photoelectric attenuation coeffi cient, uf
~ is the total Compton mass attenuation coeffi cient,Gcoh/ (!is
the mass attenuation coefficient for coher ent scattering, and "/~
is the pair-production mass attenuation coefficient.
The mass energy transfer coefficient (PKI ~) of a material for
indirectly ionizing particles is the quotient of dEK by the product
of E.~ and dl, where Eis the sum of the energies (excluding rest
energies) of the indirectly ionizing particles incident normally
upon a layer of thick ness dl and density~. and dEK is the sum of
the kinetic energies of all the charged particles liberated in this
layer.
I'K dEK - = E'i ----,;z (1.1.-3)
Notes: (a) The relation between energy fluence and kerma may be
written as
K = F PK. (1.1.-4) 1) e
(b) For X- or gamma rays of energy hv
/'K 'l'a Ga Xa -=-+-+-.
( •I ~ = the photoelectric mass attenuation coefficient, ~ =
average energy emitted as fluorescent radiation per photon
absorbed.) and
Ga a Ee -=fih.
( af e = total Compton mass Ee = average energy of the scattered
photon.) and
"• = :!...(1 _ 2mc2 )
(1.1.-8)
("/ ~ = mass attenuation coefficient for pair production, m c2 =
rest energy of the electron.)
The mass energy-absorption coefficient (Pen/e) of a material for
indirectly ionizing particles is pK/e (1- G), where G is the
proportion of the energy of secondary charged particles that is
lost to bremsstrahlung in the material.
Notes: (a) When the material is air, Pen/~ is propor tional to the
quotient of exposure by fluence 2).
(b) PK/~ and Pen/~ do not differ appreciably unless the kinetic
energies of the secondary particles are com parable with or larger
than their rest energy.
Comments: 1) The linear attenuation coefficient, linear energy
transfer coefficient, and linear energy absorption coefficient may
be obtained by multiplying the mass attenuation coefficient, mass
energy transfer coefficient, and mass energy absorption
coefficient, respectively, by the density of the material, f!·
Similarly, the various atomic attenuation, transfer and absorption
coefficients are obtained bydividingthe mass coefficients by the
number of atoms per gram.
') See Sec. 1.1.3., Eqs. (1.1.-15) and (1.1.-17). ') See Sec.
1.1.3. (d).
Ref. p. 5] 1.1. Radiation quantities and units 3
2) The expressions in the notes for /len/e and pxfe assume that
nuclear interactions are not important. An extra term for such
interactions may be required for X- or gamma-ray energies in excess
of a few MeV.
The mass stopping power Sf e of a material for charged particles is
the quotient of dEs by the product of dl and e. where dEs is the
average energy lost by a charged particle of specified energy in
traversing a path length til, and e is the density of the
medium.
S 1 dEs --e = --e (il' (1.1.-s>
Note: dEs denotes energy lost due to ionization, electronic
excitation and radiation. For some purposes it is desirable to
consider stopping power with the exclu sion of bremsstrahlung
losses. In this case S must be multiplied by an appropriate factor
that is less than unity.
The linear energy transfer (L) of charged particles in a medium is
the quotient of dEL by dl, where dEL is the average energy locally
imparted to the medium by a charged particle of specified energy in
traversing a distance of dl.
L = dEL dl
(1.1.-10)
Notes: (a) The term "locally imparted" may refer either to a
maximum distance from the track or to a maximum value of discrete
energy loss by the particle beyond which losses are no longer
considered as local. In either case the limits chosen should be
specified.
(b) The concept of linear energy transfer is different from that of
stopping power. The former refers to energy imparted within a
limited volume, the latter to loss of energy regardless of where
this energy is absorbed.
Comment: It has been suggested [ 4) that the term "locally
imparted" refer to the maximum energy loss and that this energy
loss (in eV) be noted by a sub script. Thus L 100 would be a value
of L obtained when tracks due to secondary particles (delta rays)
with ener gies of 100 eV or more are counted as separate tracks. L
00 (or LET 00) is equal to the product of mass stopping power and
density.
The average energy ( W) expended in a gas per ion pair formed is
the quotient of E by Nw, where Nw is the average number of ion
pairs formed when a charged particle of initial kinetic energy E is
completely stopped by the gas.
W=_!__, Nw
(1.1.-11)
Notes: (a) The ions arising from the absorption of bremsstrahlung
emitted by the charged particles are to be counted in Nw').
(b) In certain cases it may be necessary to consider the variation
in W along the path of the particle, and a differential concept is
then required, but is not specific ally defined here.
The specific gamma ray constant (F) of a gamma emitting nuclide is
the quotient of l' (LIXfLit) by A. where LIXfLit is the exposure
rate at a distance l from a point source of this nuclide having an
activity A and Ll has the meaning indicated in Sec. 1.1.1.
l 2LIX F= ALit. (1.1.-12)
,.
Special units of specific gamma ray constant are Rm2h-' Ci-' or any
convenient multiple of this•).
Note: It is assumed that the attenuation in the source and along
lis negligible. However, in the case of radium the value of r is
determined for a filter thickness of 0.5 mm of platinum and in this
case the special units are Rm 2h-'g-1 or any convenient multiple of
this.
1.1.3. PHYSICAL RADIATION QUANTITIES
The particle fluence 3 ) or fluence (@) of particles is the
quotient of LIN by Lla, where LIN is the number of particles which
enter a sphere•) of cross-sectional area Lla and Ll has the meaning
indicated in Sec. 1.1.1.
@~LIN Lla · (1.1.-13)
The particle flux density or flux density (</>) of particles
is the quotient of Llrp by Lit, whereLI@ is the particle flu ence
in time Lit and Ll has the meaning indicated in Sec. 1.1.1.
-!. = Lj(li p ~· 0~~~
Note: This quantity may also be referred to as particle fluence
rate.
The energy fluence (F) of particles is the quotient of LIEF by Lla,
where LIEF is the sum of the energies, ex clusive of rest
energies, of all the particles which enter a sphere4) of
cross-sectional area Lla and Ll has the meaning indicated in Sec.
1.1.1.
LIEF F =LiB' (1.1.-15)
The energy flux density or intensity (I) is the quotient ofLIF by
Lit, whereLIFis the energy fluence in the time Lit and Ll has the
meaning indicated in Sec. 1.1.1.
I= ~~. (1.1.-16)
Note: This quantity may also be referred to as energy fluence
rate.
The kerma5 ) (K) is the quotient of LIEK by Lim, where LIEK is the
sum of the initial kinetic energies of all the charged particles
liberated by indirectly ionizing particles in a volume element of
the specified material, Am is the mass of the matter in that volume
element and Ll has the meaning indicated in Sec. 1.1.1.
LIEK K = Lim . (1.1.-17)
1) This note (a} is revised. •) In regard to the abbreviation Ci
for the unit Curie see
Report on the Com. Consultatif pour les etalons de mesure des
radiations ionisantes. 4e session, 1963 (Paris, Gauthier
Villars&Co.),seeEq. (1.1.-25). ConcerningRseeEq.
(1.1.-19).
a) This quantity is the same as the quantity, nvt, com monly used
in neutron physics.
f.) This quantity is sometimes defined with reference to a plane of
area Ja, instead of a sphere of cross-sectional area Lla. The plane
quantity is less useful for the present purposes and it will not be
defined. The two quantities are equal for a uni-directional beam of
particles perpendicularly incident upon the plane area.
5) Various other methods of specifying a radiation field have been
used, e.g., for a neutron source the ufirst collision dose" in a
standard material at a specified point.
4 1. Dosimetric fundamentals and irradiation limits [Ref. p.
5]
Notes: {a) Since LIEK is the sum of the initial kinetic energies of
the charged particles liberated by the in directly ionizing
particles, it includes not only the kinetic energy these charged
particles expend in collisions but also the energy they radiate in
bremsstrahlung. The energy of any charged particles is also
included when these are produced in secondary processes occuring
within the volume element. Thus the energy of Auger electrons is
part of LIEK.
(b) In actual measurements Lim should be so small that its
introduction does not appreciably disturb the radiation field. This
is particularly necessary if the medium for which kerma is
determined is different from the ambient medium; if the disturbance
is appreciable an appropriate correction must be applied.
{c) It may often be convenient to refer to a value of kerma rate
for a specified material in free space or at a point inside a
different material. In such a case the value will be that which
would be obtained if a small quantity of the specified material
were placed at the point of interest. It is, however, permissible
to make a statement such as: "The karma for air at the pointp
inside a water phantom is ... ". Recognizing that this is a
shorthand version of the fuller description given above.
{d) A fundamental physical description of a radiation field is the
intensity {energy flux density) at all relevant points. For the
purpose of dosimetry, however, it may be convenient to describe the
field of indirectly ionizing particles in terms of the kerma rate
for a specified ma terial. A suitable material would be air for
electromag netic radiation of moderate energies, tissue for all
radia tions in medicine or biology, or any relevant material for
studies of radiation effects.
Karma can also be a useful quantity in dosimetry when charged
particle equilibrium exists at the position and in the material of
interest, and bremsstrahlung losses are negligible. It is then
equal to the absorbed dose at that point. In beams of X- or gamma
rays or neutrons, whose energies are moderately high, transient
charged-particle equilibrium can occur; in this condition the kerma
is just slightly less than the absorbed dose. At very high energies
the difference becomes appreciable. In general, if the range of
directly ionizing particles becomes com parable with the mean free
path of the indirectly ionizing particles, no equilibrium will
exist.
The kerma rate is the quotient of LIK by Lit, where LIK is the
increment in kerma in time Lit and Ll has the mean ing indicated
in Sec. 1.1.1.
The exposure (X) is the quotient of Ll Q by Lim, where LIO is the
sum of the electrical charges on all the ions of one sign produced
in air when all the electrons {nega trons and positrons),
liberated by photons in a volume element of air whose mass is Lim,
are completely stopped in air and Ll has the meaning indicated in
Sec. 1.1.1.
LIO X~ Lim. (1.1.-18)
1 R ~ 2.58·10-4 C/kg. (1.1.-19) 1)
1 ) This unit is numerically identical with the old one defined as
1 e.s.u. of charge per 0.001293 gram of air. Cis the abbreviation
for Coulomb.
Notes: (a) The words "charges on all the ions of one sign" should
be interpreted in the mathematically ab solute sense.
(b) The ionization arising from the absorption of bremsstrahlung
emitted by the secondary electrons is notto be included inLIQ.
Except forth is small difference, significant only at high
energies, the exposure as defined above is the ionization
equivalent of the kerma in air.
(c) With present techniques it is difficult to measur~ exposure
when the photon energies involved lie above a few MeV or below a
few keV.
(d) As in the case of kerma it may often be convenient to refer to
a value of exposure or of exposure rate in free space or at a point
inside a material different from air. In such a case the value will
be that which would be determined for a small quantity of air
placed at the point of interest. It is, however, permissible to
make a state ment such as: 'The exposure atthe pointp inside a
water phantom is ... ".
The exposure rate is the quotient of LIX by Lit, where LIX is the
increment in exposure in time Lit and Ll has the meaning indicated
in Sec. 1.1.1.
LIX Exposure rate ~ Lit . {1.1.-20)
The absorbed dose (D) is the quotient of Ll£o by Lim, where Ll£o is
the energy imparted by ionizing radiation to the matter in a volume
element, Lim is the mass of the matter in that volume element and
L1 has the meaning indicated in Sec.1.1.1.
.1£o D ~ Lim. (1.1.-21)
The special unit of absorbed dose is the rad.
1 rad = 100 ergfg = 1/100 J/kg. (1.1.-22)
Note: J is the abbreviation for Joule.
Comment: To avoid confusion with the abbreviation for "radian" it
is considered acceptable by ICRU to use the abbreviation "rd" for
the "rad".
The absorbed dose rate is the quotient of LID by Lit, where LID is
the increment in absorbed dose in time Lit and Ll has the meaning
indicated in Sec. 1.1.1.
Absorbed dose rate = LID . Lit
(1.1.-23)
A special unit of absorbed dose rate is any quotient of the rad by
a suitable unit of time (rad/d, rad/min, rad/h. etc.).
The activity {A) of a quantity of a radioactive nuclide is the
quotient of LIN by Lit, where tJN is the number of nuclear
transformations which occur in this quantity in time Lit and Ll has
the meaning indicated in Sec. 1.1.1.
LIN A =Lit. {1.1.-24)
1 Ci = 3.7·1010 [s- 1] (exactly). (1.1.-25)
Note: In accordance with the former definition of the curie as a
unit of quantity of a radioactive nuclide, it was customary and
correct to say: "Y Curies of P-32 were administered ... ". It is
still permissible to make such
1.1. Radiation quantities and units 5
statements rather than use the longer form which is now correct: "A
quantity of P-32 was administered whose activity was Y
Curies."
1.1.4. BIOPHYSICAL RADIATION QUANTITIES
1.1.4.1. DOSE EQUIVALENT
1. For protection purposes it is useful to define a quan tity
which will be termed the "dose equivalent", (DE).
2. (DE) is defined as the product of absorbed dose, D, quality
factor, (OF), dose distribution factor, (DF), and other necessary
modifying factors.
(DE) = D(OF) (DF) . .... (1.1.-26)
3. The unit of dose equivalent is the "rem". The dose equivalent is
numerically equal to the dose in rads multiplied by the appropriate
modifying factors.
1.1.4.2. RELATION BETWEEN LAND QF
The relation between L and QF as recommended by the ICRP is given
in the table below:
Table 1.1.-1. Relationship between L 00 and QF [ 4]
Loo [keVfl'm in water]
23 - 53 53 -175
10-20
1.1.4.3. EVALUATION OF DE
A joint committee of the ICRP and ICRU has considered the problem
of the evaluation of DE in detail. Their recommendations [ 4] are
as follows :
For a radiation involving a range of LET's the dose equivalent (DE)
may be defined as:
DE= I D(L) . OF(L) . dL, 0
(1.1.-27)
where D (L) is the actual (non-normalized) dose per unit LET
interval at the LET, L, and OF (L) is the quality factor for this
LET.
It is useful to consider the practical problem of the assessment of
DE in radiation protection surveys, since this may be carried out
in a variety of ways and the choice between these will depend on
the practical situation en countered. The accurate evaluation of
DE requires a determination of absorbed dose as a function of LET.
A technique has been devised to determine D (L) for particles other
than electrons at LET values greater than 3.5 keV(I'm. Since the OF
for virtually all electrons en countered in practice and for any
particles having LET less than 3.5 keV(I'm is equal to unity, one
may deter mine the D (L)oo above this limit and
lA
00
subtract the integral f D (L) dL from the total absorbed 3.5
dose 00
<f D(L) dL) 0
as measured with a tissue equivalent ionization chamber. In this
way it is possible to obtain the absorbed dose delivered at an LET
< 3.5 keV/1-'m which is given a OF of unity, and then to
evaluate the integral
00
f D(L)·OF(L)·dL. 3.5
The total DE is given as the sum of these two terms. This method
has the advantage that no explicit know ledge of the nature or
energy of the radiation(s) is re quired and, for this reason, it
is particularly useful in very complicated radiation fields such as
exist in the vicinity of GeV accelerators. Furthermore, because it
is the most exact method, it always results in the lowest value of
DE since simplifications must be conservative and thus lead to
overestimates. On the other hand, because of the complexity of the
method and the extensive measuring equipment requirements this
approach is, at present, rarely used.
Most practical DE problems consist in the evaluation of the hazard
due to a mixture of neutrons and gamma radiations. The OF of
neutrons as a function of neutron energy has been evaluated for
neutron energies up to 10 MeV. lithe neutron energy distribution is
known, the absorbed dose due to neutrons may then be multiplied by
an appropriate OF to obtain the DE. If the precise neutron energy
is unknown, and provided neutrons are thermal. intermediate or fast
(i.e. have energies of less than 10 MeV), the absorbed doses due to
neutrons and gamma rays may be evaluated separately. The sum of the
former multiplied by 10 and the latter multiplied by 1 may be
considered an upper limit of the DE. Finally, the simplest approach
is merely to measure the total ab sorbed dose and multiply it by a
OF of 10. While being the simplest, this method may result in an
overestimate that can be as high as 10.
Comment: This formulation is applicable to dose equi valents of
magnitudes that are less than or comparable to the maximum
permissible dose equivalent. At higher doses dose rate and other
factors are important, but there are as yet no firm recommendations
in this area.
References [1] L. S. TAYLOR: History of the International
Com
mission on Radiological Units and Measurements (ICRU). Health
Physics 1, No.3, 306 (1958).
[ 2] Recommendations of the International Commission on
Radiological Units. Radiology 62, No. I, 106 (1954).
[J] Recommendations of the International Commission on Radiological
Units and Measurements, Report No. lOa on Radiation Quantities and
Units. Natio nal Bureau of Standards Handbook 84, Washing ton
1962.
[ 4] Report of the RBE Committee to the International Commissions
on Radiological Protection and on Radiological Units and
Measurements. Health Physics 9, No.4, 357 (1963).
[5] F. B. SILSBEE: Systems of Electrical Units. U. S. National
Bureau of Standards, Monograph 56.
6 1. Dosimetric fundamentals and irradiation limits [Re£. p.
11
1.2. IRRADIATION LIMITS by J. MEHL
1.2.1. GENERAL CONSIDERATIONS The purpose of a radiation shield is
to protect
objects that can suffer radiation damage where the irradiation can
not be made less by reducing the sources' strengths, by reducing
the irradiation times, or by increasing the separations between
source and objects.
In order to permit adequate shielding at reason able cost, due
consideration should be given to radiation levels which can be
considered not to involve unacceptable radiation effects. Such
radiation levels depend upon the response to irradiation ofthe
particular object for which protec tion is required and on the
definition of the accept able radiation effect.
1.2.1.1. RESPONSE OF OBJECTS TO IRRADIATION
There exists a significant difference in the radia tion effects in
inanimate and animate objects. For inanimate objects, irradiation
results in effects that manifest themselves temporarily or
permanently in the irradiated object only; however, for animate
objects, injuries may manifest themselves also in their
descendants. Thus, in particular where ex posure of man must be
considered, limitation of radiation levels must be governed by
both, considera tion of radiation effects in the individual
(somatic effect) and by consideration of effects to the popu
lation (genetic effects). Normally, the response of the particular
object under consideration differs with
(i) the part of the object which is irradiated, (ii) the radiation
quantity,
(iii) the radiation quality, and (iv) the mode of
irradiation.
If irradiation of man (or animate objects) is con sidered for the
assessment of genetic effects, also ( v) the number of individuals
subjected to radiation
and that are capable of producing descendants must be taken into
account.
Irradiation of parts of the object may need conside ration where
the object is or could possibly be near the source or within a
collimated radiation beam and where shielding can be provided only
for parts of the object. Normally, irradiation of the object as a
whole is of interest where the object is remote from the source or
in a diffuse radiation field.
The radiation quantity referred to above depends upon the source
strength, the source-to-object geo metry'), the efficiency of
shields and the time period during which the object is actually
irradiated: The assessment of these factors may be complex
where
(i) the source strength varies with time, (ii) the source or the
object moves;
1) Unless the object is within a diffuse radiation field.
(iii) the number of sources or the number of objects which need
protection exceeds unity,
and in particular where any combination of (i) - (iii) must be
considered.
If the source strength varies, averaging proce dures can be
applied. However, if the source or the object moves, numerical
values of acceptable radiation levels which are applicable to the
indivi dual object may be of little help to the designer of
radiation shields. If the source is moving, it is preferable that
an area around the source be defined beyond which the accepted
radiation levels should not be exceeded. If the object is moving
within a defined area, it is useful that radiation levels within
that area do not exceed accepted limits.
Radiation quantities and units defined by ICRU (see Sec. 1.1.3.) to
which reference should be made here are:
(i) exposure, X [R], (ii) absorbed dose, D [rad],
(iii) kerma, ]{ [MeVfg], (iv) energy fluence, F [MeVjcm2], and (v)
particle fluence, <P [particlesorphotonsfcm2]
being the time integrals of
exposure rate [R/s], absorbed dose rate [ radjs], kerma rate [MeVjg
s], energy flux density [MeVjcm' s], and particle flux density
[particles orphotonsjcm's]
respectively. Design of shields is normally based on values of the
flux density which apply to locations of particular interest
between source and object (see Sec. 1.3.). Values of the absorbed
dose are assessed where the response of irradiated objects to
radiation depends on the energy absorbed per unit mass. Use of the
kerma may be necessary where indirectly ionising particles (e.g.
neutrons) interact with matter. For X- and gamma-radiation above a
few keV up to 2 MeV data expressed in exposure values are often
preferred in order to facilitate con trol by measurement.
Differences in energy imparted to matter per particle or photon, or
differences in microscopic distribution of the absorbed energy do
not affect the absorbed dose value unless the energy absorbed per
unit mass is changed. Therefore the absorbed dose will be
unsuitable for purpose of radiation protection where the radiation
effects, either mani fest themselves only if the energy imparted
per particle or photon exceeds certain threshold values or depend
upon the microscopic distribution of th~ absorbed energy. In such
cases additional factors need to be taken into account which depend
upon the radiation quality.
The radiation quality is defined by the radiation type and the
particle or photon energy. Absorption and scattering affects the
radiation quality. It is therefore subject to variation as
particles or pho-
Ref. p. 11] 1.2. Irradiation limits 7
tons interact with matter on their track from the source to the
object under consideration.
Due to the microstructure of biological tissue its response to
radiation depends upon the microscopic distribution of the absorbed
energy. Experimental findings have proven that the response of
biological tissue is related to the linear energy transfer (LET).
Based upon LET values which apply to specific radiation types and
particle or photon energies, quality factors, QF, were recommended
by ICRP [I] which if multiplied by the corresponding ab sorbed
dose value result in a quantity that expresses on a common scale
for all ionizing radiations the irradiation incurred by persons.
The name re commended by ICRU for this quantity is the "dose
equivalent", its unit the "Rem". The radiation quantities and units
listed above should therefore be supplemented by
(vi) dose equivalent, DE [rem] (see Sec. 1.1.4.)1).
Numerical values of QF are given in Sec. 1.1.4.2., Table 1.1.-1,
and Sec. 1.3., Tables 1.3.-1 and 1.3.-6. It should however be
pointed out here that the QF values listed in these tables do not
necessarily apply to all animate objects and do certainly not apply
to inanimate objects.
The mode of irradiation i. e. the way in which the radiation
quantity is fractionated and the rate at which each fraction is
given are known to affect somatic effects due to irradiation of man
and most of the animate objects. However, it appears from
theoretical and experimental studies that when either the total
accumulated dose received or the dose rate is very low any somatic
effects will be directly proportional to the total dose and
independent of the dose rate.
A linear dose-effect relationship unaffected by dose rate is in
general assumed for gene-mutations. Only at intermediate and higher
levels of dose rate may gene-mutations not be independent of the
dose rate. Thus, after consideration of the mode of irradiation the
dose equivalent still can be accepted as a radiation quantity
suitable for purposes of radiation protection of man.
Radiation effects in inanimate objects may also be affected by the
mode of irradiation. The response of the object under consideration
rna! significantly differ from that of man and most am mate
objects so that detailed investi~ation ~ay ~e indicated if no
information on thts question lS
readily at hand.
Where genetic effects are involved the number of individuals which
need. c.o:'sideration may. be taken into account by defm1t10n of a
population dose average that is relevant to the assessment of
genetic injury to the whole population. The nu~er~ cal value of
that population dose average whtch lS
considered acceptable may be made up by quotas assigned to various
groups of the population, each group being made up by individual~
which have a similar standing with respect to bemg exposed to
1) The maximum permissible doses (M PD) are given as dose
equivalents in "rem".
lA'
ionizing radiation and the exposure levels which can be
permitted.
It is obvious that the efficiency of shields should be judged upon
by reduction factors which apply to that radiation quantity which
can best-where ne cessary with appropriate factors such as the
quality factor- be related to the response of the object to
radiation of the specific quality under consideration. Expert
advice may be required for proper specifica tion of shielding
requirements as well as for proper interpretation of shield
efficiences, where the re sponse of the object to radiation is
complex.
1.2.1.2. ACCEPTABLE RADIATION EFFECTS The problem involved in the
assessment of the
radiation effect which can be accepted for a parti cular object is
to find a reasonable balance between the drawbacks and the benefits
which would result from the acceptance of the effect.
Where irradiation results from uses of radiation sources for the
benefit of mankind the governing principle is to balance these
benefits against the radiation risk to man. Somatic radiation
effects in man which can be considered accept able depend on
factors which do not significantly vary between members of
different races and popu lations. Therefore it is possible for
acceptable radia tion effects to be agreed upon internationally.
However, in the case of genetic effects the factors required to
find a proper balance between risks and benefits vary from country
to country so that the final decision on acceptable effects must
rest with each country.
Also in the case of consumer goods, if they are extremely sensitive
to ionizing radiation and if they are used throughout the world it
may be desirable that agreement on acceptable radiation effects be
achieved at an international level (e. g. photographic film). Where
protection of the object is required for technical reasons, the
advantages achieved by the reduction of the radia tion effect are
to be balanced against the costs of the protectives measures. In
such cases the accept able effect depends upon the technical needs
and can be assessed only for each particular case in
question.
1.2.2. PROTECTION OF MAN Provision of adequate protection of man
against
the hazards of ionizing radiation is the common objective of all
nations having an interest in uses of radiation. For that reason
the work of the Inter national Commission on Radiological
Protection (ICRP) which originated in the Second Internatio nal
Congress of Radiology in 1928, was supported by many countries. The
recommendations of the Commission on the basic principles of
radiation pro tection of man [J] served as a basis in the esta
blishment of conventions, basic safety standards and
recommendations of the specialized Agencies of the United Nations
[4] [International Labour Office (ILO), International Atomic Energy
Agency (IAEA)] [ 5] and in the establishment of regional
8 1. Dosimetric fundamentals and irradiation limits [Ref. p.
11
and national regulations on radiation protection. Therefore shield
design for purposes of protection of man will, in general, rely on
the basic recommen dation of ICRP.
1.2.2.1. MAXIMUM PERMISSlliLE DOSE EQUIVALENTS
The basic concept of ICRP is to ensure protection of health by
deriving from previous experience, experimental data and
theoretical studies "maxi mum perrnissible doses" (M PD) so that
doses which are below these values "involve a risk that is not
unacceptable to the individual and to the popula tion at large".
Consequently, doses which are below the maximum perrnissible values
should be considered perrnissible or acceptable. The concept of the
MPD can be applied only if the rates by which these doses are
received are low. For that reason it was necessary to supplement
111 PD values by inforrnation on the time during which these doses
can be received. The recommendations are designed to limit somatic
and genetic effects. There fore it was necessary to reduce both
the dose to the population as a whole as well as the dose to the
individual as much as possible. This is done by
(a) Classification of exposed individuals into the following two
categories :
(i) Adults irradiated in the course of their work.
(ii) Members of the public (this group comprises among others
adults and children living in the neighbourhood of radiation
areas).
(b) The establishment of MPD values for indi viduals of each
category.
(c) The establishment of a maximum permissible genetic dose to the
whole population which is to be made subject to proper
apportionment between various categories of individuals.
The genetic dose to a population is assessed as the annual
genetically significant dose multiplied by the mean age of child
bearing. The annual genetically significant dose to a population is
the average gonad dose weighted for the expected number of
children.
The time period of irradiation on which theM PD values are to be
based depends upon whether somatic or genetic effects are to be
considered. Where somatic effects need consideration in radiation
protection practice, any time period up to the lifetime of the
individual is of interest. In cases where genetic effects to the
population are of particular concern, the time period of
irradiation on which M P D values are based is the mean age of
child bearing which is normally taken to be 30 years.
It is not possible in the design of shields to take into account
the special conditions under which, in ICRP regulations, allowance
is made for higher doses (e. g. if the dose accumulated from
previous irradiation is low, or if only a part of the body is
irradiated). Maximum permissible dose values re commended for
purposes of planning and design are derived from the maximum
permissible annual doses
which apply to whole body irradiation and are given
astheweeklyaverageofthat dose (see Table 1.2.-1).
Table 1.2.-1. Maximum permissible annual dose equi valentsa) for
whole-body irradiation
Category Annual MPD [rem]
in the course of their work
Mem hers of the public 5 0.5
1/10 1/100
Annual genetically significant doseb) to the population 5/30
1/300
a) These values do not include doses received from medical
procedures and from natural background radiation.
b) Allocations of this dose among the various categories of
individuals depend on factors which are different from country to
country. Therefore the decision must rest with the competent
national authorities.
It is to be noted that the Commission decided to exclude from the
proposed values contributions from medical procedures and from
natural back ground radiation. This was necessary because these
contributions vary considerably from country to country. However,
the Commission recommended that these contributions should be
considered sepa rately and that contributions from medical proce
dures should be limited to a minimum value con sistent with
medical requirements.
In Table 1.2.-2 are listed the maximum perrnis sible annual doses
which include allowances that
Table 1.2.-2. Maximum permissible annual dose equi valents for
partial-body irradiation
Organ
Gonads, red bone marrow, and in the case of uniform irra diation,
the whole body
Skin, thyroid, bone Hands, forearms,
feet, ankles All other organs
Category of individuals Adults Members
irradiated of the in the course public of their work
[rem] [rem]
75 15
0.5 3
7.5 1.5
can be applied if the exposure of the individual is essentially
restricted to portions or single organs of the body.
These values are primarily used in limiting inter nal radiation
but can also be of guidance in such cases where shielding can be
provided only for parts of the body, e. g. for the trunk of the
body but not for the hands or the head of the individual.
Ref. p. 11] 1.2. Irradiation limits 9
1.2.2.2. TECHNICAL AND OPERATIONAL STANDARDS
The primary objective which should be achieved by technical and
operational standards is the deri vation of minimum requirements
of structural and operational protection so that under conditions
of normal operation, irradiation of persons \vould not result in
doses in excess of M PD-values.
Naturally, these requirements depend upon the type of source, the
type of operation and the con ditions under which the operation in
question is performed. It is of course not possible to consider in
detail all the various types of sources which are now in use and
the numerous operations for which they are used. Also it is not
possible to predict in detail the conditions under which all the
various operations will be perfomed in which ionising ra diation
is involved. Therefore it was necessary to demand that operations
with ionizing radiations should only be permitted if a number of
minimum requirements of operational protection are fulfilled which
reflect on :
(i) the administrative organisation, including a system by which
notification, registration, li censing, recording, inspection and
intervention are governed,
(ii) the physical and medical surveillance of indi viduals and the
population, including a system by which the establishment of
controlled areas, individual monitoring, area monitoring, en
vironmental monitoring, waste processing and medical tests are
governed.
Fundamental principles on which the administra tive organisation
and the medical and physical sur veillance should be based are
contained in the basic recommendations of ICRP [3], the convention
and recommendations of ILO [ 4], and the basic safety standards of
IAEA [5]. These principles have been adopted in most national
standards. Therefore, in determining special requirements of
structural and operational protection for specific sources and ope
rations, it can be assumed that the operations are performed in
compliance with these minimum re quirements of operational
protection. This leaves a certain flexibility to balance adequately
the de gree of the structural protection and the degree of
operational protection to be applied to operations and sources
which are suitable for more detailed consideration. Detailed
international recommen dations and standards are primarily
intended to facilitate procedures of licensing of sources to be
applied throughout the world and of operations to be performed
everywhere in the world in order to permit that all countries can
benefit from the use of ionizing radiation under safe conditions.
This applies in particular to
(i) sources which can be exempted from licensing procedures,
(ii) medical radiation sources and their operation for therapeutic
and diagnostic purposes re spectively,
(iii) industrial radiation sources and their opera tion, and
(iv) the international transport of radioactive materials.
Technical and operational standards which give detailed information
on structural and operational protection requirements against risks
of exposure to external radiation are contained in reports of ICRP
Committees [ 6, 1], detailed operational stan dards of IAEA [ 8,
9] and safety regulations of ILO [ 1 OJ. These standards are kept
continually under. review and are periodically subject of revi
sion. Therefore the reader is advised to check whether numerical
data, to which reference is made in this section are still in
compliance with the most recent recommendations of the respective
organi sations.
\Vhcre the type of source and the respective operations are well
defined it is possible to lay down the minimum requirements of
structural pro tection which should apply to the containment of
the source. In the establishment of numerical values due
consideration is given to the following aspects of each source and
operation in question
(i) the distance of areas around the source to which access of
persons is required,
(ii) the category of persons for which access to the areas is
required and the contribution to the respective lvl PD which can be
permitted from the source under consideration,
(iii) the average amount of access time required for persons of the
category in question to the area under consideration (occupancy
factor).
In Table 1.2.-3 are listed maximum and average exposure rates of
leakage radiation in the vicinity of radiation sources which for
the indicated operations comply with the standards.
Minimum requirements of structural protection to be provided
through primary and secondary barriers to attenuate the useful beam
and the stray radiation depend in addition to the factors referred
to above on the following factors:
(iv) The average radiation output of the source at which it will be
operated (work load factor), and
(v) the fraction of the work load during which the useful beam is
pointed in the direction of the occupied area under consideration
(use factor of the barrier).
Therefore, for installations which are similar in type, it is in
general not possible to express the requirements of the respective
barriers in numerical values applicable to all installations of
that type. Such values must be calculated separately for each
installation. Detailed guidance on these calcu lations has been
provided by ICRP for protective barriers for X- and gamma rays [
6]. Since it is inevitable that these calculations arc based on
assumptions, it is necessary to obtain evidence of their validity
by methods of physical surveillance. For that reason detailed
standards on structural protection arc supplemented by detailed
standards on operational protection which prescribe in more detail
adequate measures of physical surveillance
10 1. Dosimetric fundamentals and irradiation limits [Ref. p.
11]
Table 1.2.-3. Maximum and average exposure rates of leakage
radiation in the vicinity of radiation sources which comply with
standards of reference
Type of source I Type of operation Area of reference Exposure rate
Reference
Ionising radiation any 11ormal not 0.1 m from surface max. < 0.1
mremfh IAEA Safety Series exempted by the of apparatus No. 9 (1962)
p. 23, standards para. 5.1.1.4 (iii) without licensing
TV set normal for use by 0.05 m from surface max. < 0. 5 mRfh
ICRP Pub!. 3 (1960) the public of set p. 14, para. 119;
IAEA Safety Series No. 9 (1962) p. 23, para. 5.1.1.4 (v)
Medical X- or lektherapy 0. 0 5 m from surface max. < 100 mRfh
ICRP Pub!. 3 ( 19 60) gamma-ray beam control in of source housing
av. < 20mR/h p. 3 and p. II, para. >IOOkV "off" position 1. 0
m from source max.< 10mR/h 82; ICRP Pub!. 4 useful beam av. <
2mR/h (1964) p. 8, para. > 100 R/h at I m 55-56
teletherapy 1 m from source max. < I R/h or beam control in
except diaphragm 0.1% of useful beam, "on" position region dose
rate at 1 m
from the source transmission of < 5% of useful diaphragm beam
dose rate
Medical X- or teletherapy 0. 0 5 m from surface max. < 200 mRJh
gamma-ray beam control in of source housing av. < 40mRfh
>100kV "off" positions) 1 m from source max. < I 0 mR/h
useful beam av. < 2mR/h <100 Rfh at 1m
Medical X-ray therapy at every 5 em from surface max.< 30 Rfh
ICRP Pub!. 3 (1960) specified rating of of tube housing at p. 5
tube any point accessible
to patient 1 m from focus max.< 1 R/h
Medical X-ray diagnosis at every 1 m from focus max. < 100 mRfh
ICRP Pub!. 3 (1960) specified rating of p. 4 tube
Industrial X- or unspecified normal 0. 0 5 m from surface max. <
100 mR/h") ICRP Pub!. 3 (1960) gamma ray beam control in of source
housing av. < 20 mRjh•) p.4; ICRP Pub!. 6
"off" positions) 1 m from source max. < 10 mR/hb) (1964) p. 70
av. < 2 mRfh•)
Industrial X-ray X -ray analysis at 0. 0 5 m from surface max. <
25 mRfh ICRP Pub!. 3 (1960) every specified of tube housing p. 13,
para. 106 rating
X-ray high-voltage normal use 0.05 m from surface max. < 20 mRfh
ICRP Pub!. 3 (1960) generator of housing p. 7, para. 40
occupied space within a controlled
max.< 2mRfh
area
Radioactive transport in com- external surface of max. < 0.5
mRfh•) IAEA Safety Series as specified in pliance with regula-
package No. 6 (1964, revi- the regulations tions applicable to sion
1965) para.
Category I packages C-3.4 in compliance with external surface of
max. < 10 mRfh•) regulations applic- package able to Category II
1 m from centre of max. < 0. 5 mRfh•) packages package in
compliance with external sudace of max. < 200 mR/h') regulations
applica package able to Category III 1 m from centre of max. <
10 mRjh•) packages package
a) No numerical values recommended for beam control in "on"
position. b) Exemption from these specifications may be permitted
according to ICRP Publ. 6. C) For large external dimension packages
( > 2m), fissile packages and low specific activity materials
loads maximum ex
posure rates apply which differ from those listed in this
table.
1.2. Irradiation limits 11
to be applied to operations which have been sub jected to detailed
consideration. It is obvious that radiation safety is only
maintained where evidence can be obtained that the operations arc
performed in compliance with both, the requirements of structural
and of operational protection.
Since the provision of detailed information on the design of
adequate shields is the primary objec tive of this compendium,
reference to the methods of calculation of the "allowable
transmission" of shields is left to the respective chapters of this
book. However, it is felt that the reader should be reminded in
this section of some basic principles recommended by ICRP [6] by
which the determi nation of operational protection requirements
appli cable to radiation installations should be governed:
(i) Plans for new installations using ionising radia tion or
modifications of existing installations involving structural
shielding should be re viewed by the appropriate protective
organi sation or a qualified expert before building is
commenced.
(ii) The final plans of an installation should indi cate the types
of materials and the dimensions of all protective barriers. The
positions of all windows, doors, pipes andlouvcrersshall be indi
cated in so far as they affect the protection requirements. Such
plans should have the approval of the appropriate protection
organi sation or a qualified expert.
(iii) Routine operation shall be deferred until a radiation survey
has been made and the instal lation found to comply with the
applicable standards. The survey shall be made by the appropriate
protection organisation or a quali fied expert. A reappraisal of
the protection shall be made after every change in an existing
installation. (Change is construed to mean any change that is
likely to increase the radiation hazards, such as increase of work
load, use factor, energy of radiation or alteration of pro tective
barriers.) The installation should be resurveyed periodically to
check that condi tions are still safe. The results of a survey
should be submitted in a formal written report.
1.2.3. PROTECTION OF GOODS, MATERIALS AND DEVICES
1.2.3.1. INTERNATIONAL RECOMMENDA TIONS AND STANDARDS
Fortunately there are only few consumer goods used throughout the
world that are so sensitive to irradiation that agreement on
acceptable radiation effects and on standards of protection is
required at an international level. In fact to date reference is
made in recommendations and standards of international
organisations only to unprocessed photographic emulsions. The
response of photo graphic emulsions to ionising radiation depends
largely upon the type of emulsion and the radiation quality. The
acceptable radiation effect must be judged upon the purpose for
which the emulsion
is used. Therefore it is difficult to recommend numerical values
which apply to all emulsion types and to all types of
radiation.
In the transport regulations of IAEA [9] it is laid down that
packages containing radioactive material "shall be kept separated
from undeveloped photographic films and plates so that these are
not exposed to more than 10 mR".
In ICRP recommendations [6] it is noted that "unprocessed
photographic emulsions may be dam aged by exposure to as little as
1 mR". The diffe rence in these values is probably due to the fact
that the ICRP value considers the lower energies to which
photographic emulsions are most sensitive. These energies can
normally be ecxluded from con sideration where only that radiation
is of real con cern which penetrates the walls of a transport
container.
It is obvious that the radiation exposure is not a very suitable
measure to define the acceptable radiation effect to photographic
emulsions. How ever, more precision in the definition of
acceptable effects would lead to a system of measurements which is
difficult to apply in radiation protection practice.
1.2.3.2. SPECIAL REQUIREMENTS
Specification of structural protection require ments may have to
take into account the protection of special goods, materials and
devices within the installation. At some locations radiation levels
even lower than those which can be permitted for adequate
protection of man may be required. Typical examples are locations
of devices for low level radiation measurement. The minimum de
tectable level of the radiation to be measured by such devices may
be severely affected if the level of background radiation is
increased or is subject to significant change. It may be necessary
to per form a detailed analysis on the response of the instrument
to the expected quality of background radiation and to specify a
shielding requirement based on the maximum level of background
radia tion which can be permitted without affecting severely the
performance of the measurements in question.
At locations within useful radiation beams or within high level
radiation fields, structural pro tection may be indicated to
prevent radiation damage of goods, materials and devices which
would not withstand exposure at the levels in question over the
total length of the time during which they may be exposed. This
applies to activation of materials by thermal neutrons, and the
structural changes of substances owing to exposure to high
radiation levels. Lists of materials grouped accord ing to
radiation levels above which radiation dam age may occur are
listed elsewhere in this compen dium.
References
[I] Report at the RBE Committee to the International Commission on
Radiological Protection. Health Physics 9, 357-386 (1963).
12 1. Dosimetric fundamentals and irradiation limits [Ref. p.
19
[ 2] Recommendations of the International Commis~ sian on
Radiological Units ancl Measurements, Report Ko. lOa on Radiation
Quantities and Units. ~ational Bureau of Standards Handbook 84,
Washington 1962.
[3] Recommendations of the International Commis sion on
Radiological Protection. (Adopted Septem ber 17, 1965). ICRP
Publication 9, London: Per gamon Press 1966.
[ 4] Manual of Industrial Radiation Protection, Part L Convention
and Recommendation. International Labour Office, Geneva 1963.
~5] Basic Safety Standards for Radiation Protection, Safety Series
No. 9 (first revision). International Atomic Energy Agency, Vienna
1965.
[6] Report of Committee III on Protection Against X-Rays up to
Energies of 3 :MeV and Beta- and
Gamma~Rays from Sealed Sources. ICRP Publi cation 3, London:
Pergamon Press 1960.
[ 7] Report of Committee IV on Protection Against Electromagnetic
Radiation Above 3 MeV and Elec trons, Neutrons and Protons.
(Adopted 1962 with revisions adopted 1963). ICRP Publication 4,
London: Pergamon Press 1964.
I 8] Safe Handling of Radioisotopes. Safety Series No. 1 (first
edition with revised Appendix I). International Atomic Energy
Agency, Vienna 1962.
(9J Regulations for the Safe Transport of Radioactive Materials.
Safety Series No. 6 (1964 Revision). International Atomic Energy
Agency, Vienna 1965.
[ 1 OJ Manual of Industrial Radiation Protection, Part II: Model
Code of Safety Regulations (Ionising Radia tions). International
Labour Office, Geneva 1959.
1.3. RELATIONSHIP BETWEEN DOSE EQUIVALENT (ABSORBED DOSE) AND
FLUENCE (FLUX DENSITY)
by N. G. GoussEv
For reasons explained in detail in Sec. 1. 2. \veekly averages of
the maximum permissible doses recom mended for purposes of
planning and design (see Tables 1.2.-1, -2) arc given in units of
the dose equiv alent [rem]. However, the design o£ shields is, in
general, based upon calculations of radiation quantities such
as
(i) the particle fluence [number of particles or photonsfcm2]
or
(ii) the energy fluence [MeVfcm2].
Therefore it is necessary to find the appropriate relationship
between the respective radiation quantities.
Table 1.3.-1. Quality factors (QF) for converting absorbed doses to
dose equivalents; recommended
by ICKP
Type of radiation IQF I Type of radiation I QF
Gamma rays Thermal neutrons 3.0 X-rays Neutrons, 6 ke V 2.5
Electrons ~eutrons, 20 keV 5.0 Positrons Neutrons, 100 keV 8.0 Beta
rays :Neutrons, 500 keV 10.0 Alpha particles 10 Neutrons, 1 MeV
10.5 Protons 10 N cutrons, 5 :\fe V 7.0 Heavy recoil atoms 20
Neutrons, 10 MeV 6.5
It should be made clear right at the beginning of this section that
there exists to date no com pletely reliable or recommended
mathematical model to correlate these quantities. The formulas and
the tabular data obtained by them presented in this section are
only intended for guidance. More precision will be achieved as
further knowledge is acquired. The relationship between the dose
equiv alent and the absorbed dose received from external radiation
was discussed above. The quality factors given in Table 1.3.-1 are
used in this section for converting absorbed doses to dose
equivalents.
\Ve shall now consider the relationship between
(i) the absorbed dose (D) measured in rad (in air) and the particle
fluence (<P) measured in par ticles or photonsfcm2 or the
energy fluence (F) measured in MeVjcm2, or
(ii) the absorbed dose rate (P) measured in radfs (in air) and the
particle flux density (if;) measur ed in particlesfcm2s or the
energy flux density (/) measured in MeVfcm2 s
and determine the values <P0 , F 0, ¢0 and I 0 which correspond
to the weekly average of the M P D applicable to workers directly
engaged in radiation work (0.1 rem per 168 h week or per 40 h week,
respectively).
1.3.1. THE RELATIONSHIP BETWEEN ABSORBED DOSE
RATE (IN AIR) AND PARTICLE FLUX DENSITY OR ENERGY
FLUX DENSITY (X- AND GAMMA RAYS)
The relationship between the absorbed dose rate P and the particle
flux density if; or energy flux density I for monoenergetic
radiation of energy E [MeV per gamma quantum] under conditions of
electron equilibrium is determined by the following formula:
¢ ·E ·fJa ·1.6· lo-6
~if; 1.6 ·10-8 I fJa [radfs], (1.3.-1) where
fia is the mass absorption coefficient of gamma rays in air
[cm2jg], sec Table 4.1.-9,
1.6 ·to-6 is the energy equivalent in ergs of 1 :\'IeV, 100 is the
energy equivalent in ergjg of 1 rad.
The results of calculations performed in [I] for the particle and
energy fluences (<P and F), and the particle and energy flux
densities (if; and I) cor-
Ref. p. 19] 1.3. Relationship between dose equivalent (absorbed
dose) and fluence (flux density) 13
Table 1.3.-2. Energy fluence F 0 [MeVJcm2 or ergjcm2] which
corresponds to an absorbed dose of 0.1 rad, and energy flux density
10 [MeVfcm2 s] or particle flux den sity ¢0 [quantafcm2 s] which
corresponds to an absorbed dose rate P 0 = 2.5 mrad/h
( ~ 0.1 rad/ 40 hjwcek)
Dose of 0.1 rad Dose rate of 2. 5 mrad/h corresponds to corresponds
to
E fla F, [MeV] [cm2jg] pieVjcm2]
0.01 4.54 1.38 ·106 0.015 1.25 5.00·106 0.02 0.502 1.24·107 0.03
0.145 4.31· 107 0.04 0. 0622 1.00·10 8
0.05 0.0376 1.66· 108 0.06 0.0287 2.18·108
0.08 0.0234 2.67· 108
0.10 0.0233 2.68 ·108 0.15 0.0268 2.33·108 0.3 0.0288 2.17
·108
0.4 0.0296 2.11·108
1.0 0. 0280 2.23·108 1.25 0. 0268 2.33·108
1.50 0.0256 2.44· 108
2 0.0238 2.62· 108
3 0.0211 2.96·108
6 0.0172 3.63. 108
10 0.0153 4.08·108
15 0.0142 4.40· 108
20 0.0137 4.56· 108 30 0.0136 4.60·108 40 0.0136 4.60· 10' 50
0.0137 4.56· 108 60 0.0139 4.50. 108
80 0.0143 4.37 ·108
200 0.0162 3.86·108 300 0.0169 3. 70·108
400 0.0173 3.61·108
500 0.0175 3.57 ·108
600 0.0176 3.55 ·108
800 0.0178 3.51· 10 8
1 000 0.0179 3.49. 108
1 500 0.0181 3.45. 108
2 000 0.0182 3.43·108
3 000 0.0183 3.42·108
4 000 0.0184 3.40·108 5 000 0.0186 3.36·108 8 000 0.0187
3.34·108
10 000 0.0188 3.32·108
responding to a specific value of the absorbed dose (D) and of the
absorbed dose rate (P), respec tively, are presented in Table
1.3.~2 (see also Fig. 1.3.~1).
It should be noted that, strictly speaking, Eq. (1.3.~1) can be
used only up to a gamma radia tion energy of 3 MeV, i.e. in that
range for which the definition of the exposure (X) applies.
At higher energies, where electron cquilibriun1 is difficult to
attain, on1y very approximate calcu-
I
2.21 9.56 956 8.00 34.7 2 310
12.4 86.4 4 320 43.1 299 9 980
160 698 17 400 266 1150 23 100 349 1510 25 200 427 1850 23 200 429
1860 18 600 373 1620 10 800 347 1510 5 020 338 1470 3 660 336 1460
2 920 338 1470 2 440 346 1500 1 880 357 1550 1 550 373 1620 1 300
390 1700 1 130 419 1820 912 474 2060 686 515 2240 559 552 2400 480
581 2520 420 626 2710 339 653 2840 284 704 3060 204 730 3170 158
736 3190 106 736 3190 79.8 730 3170 63.4 720 3120 52.0 699 3040
37.9 685 2970 29.7 645 2800 18.7 618 2680 13.4 592 2570 8.56 578
2510 6.27 571 2480 4. 96 568 2460 4.11 562 2440 3.05 558 2420 2.42
552 2400 1.60 549 2380 1.19 547 2370 0. 790 544 2360 0.590 538 2330
0.467 534 2320 0.290 531 2310 0.231
lations are possible with Eq. (1.3.~1); in Fig. 1.3.~1, therefore,
the curves are drawn as broken lines after an energy of 3 MeV is
reached.
It can be seen from Fig. 1.3.~1 that in the medium-to-high energy
range the particle flux density ¢y, corresponding to a specified
absorbed dose rate, falls almost linearly as energy increases,
whereas the energy flux density I Y in this range hardly varies
\vith energy.
For medium and high energies it may be assumed
14 1. Dosimetric fundamentals and irradiation limits [Ref. p.
19
that the energy flux density I 0 corresponding to a dose rate of
0.1 rem/40 h week (2.5 mremfh) is ap proximately
I, ~ 2500 MeVfcm2s or 3.2·1o-• ergfcm2 s.
To a dose of 0.1 rem corresponds an energy fluence
F 0 = 3.6·108 MeVfcm' = 580 ergfcm'.
1.3.2. THE RELATIONSHIP BETWEEN ABSORBED DOSE
RATE (IN AIR) AND FLUX DENSITY OF BETA PARTICLES AND
MONOENERGETIC ELECTRONS IN BIOLOGICAL TISSUE
For monoenergetic electrons the relationship between particle flux
density </> [electronsfcm2 s] and dose rate P [radfs] at the
surface of biological tissue is given by the Eq. (1.3.-2)
_I_(E!._) MeVcm' 1. 6 . 10_,~ ¢em's dx g MeV d/
P= [ra s], 100 erg
g rad (1.3.-2)
where dEfdx is ionization loss of electron energy in biological
tissue [in MeVcm'fg], which can be calculated with BETHE's
well-known ionization loss formula').
The quantitative relationship between dose and fluence for
monoenergetic electrons in the energy range from 0.01 to 10 MeV was
found in [I].
The composition of the biological tissue was taken to be: H- 10%,
C- 12.3%, N- 3.5%, 0- 72.9%. The numerical values of dEfdx for the
different elements were taken from [ 2]. The calculated
relationships between the dose equiv alent, and fluence for
monoenergetic electrons