Comparitive Nuclear Effects of Bio Medical Interest

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Y  3. A t7 22 /C E  * A F C M ^C H  REPO R T A EC Ca t egory : HE ALTH  A N D SA F E TY D o cumen t s  Co l le c t! F E B 1 8 C O M P A R A T IV E  N UCLE A R E F F ECTS O F BI O M E D I C A L IN T EREST C l a y t o n S . Wh ite,  I. G e r a l d Bo wen,  Do n a ld  R . R ic hmon d , an d R o bert L Cors b ie Issuan ce Da t e: Jan uary 12 , 1 96 1

Transcript of Comparitive Nuclear Effects of Bio Medical Interest

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Y 3. At7

22/CE *

AFC

M^CH R E P O R T

AEC Category: HEALTH  AND SA FETY

Documents  Colle

F E B 18

COMPARATIVE  NUCLEAR E F F E C T S

OFBIOMEDICAL IN TEREST

Clayton S . White,  I. Gera ld Bowen , Donald   R . Ric hmond , and Rober t L Corsb ie

Issuance Date: January 12, 196 1

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NOTICE

This report is published in the interest of providing information which may prove of

value to the reader in his study of effects data derived principally from nuclear weapons

tests.

This document is based on information available at the time of preparation which

may have subsequently been expanded an d re-evaluated* Also, in preparing this reportfor publication, some classified material m ay have been removed. Users are cautioned

to avoid interpretations an d conclusions based on unknown or incomplete data*

PRINTED IN USA

Price $1.00. Available from the Office of

Technical Services, Department of Commerce.

Washington 25 , D . C.

USAEC Office of Technical Information ExtensionOak Ridge, Tennessee

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COMPARATIVE N U C L E A R E FFE C T S

OF BIO MEDIC A L I N T E R E S T

ByClayton S. White, I. Gerald Bowen,Donald R . Richmond, and Robert L. Corsbie

Approved by : R . L . CORSBIE

Director

Civil Effects Test Operations

Lovelace Foundation for Medical Education an d Research,

Albuquerque, N . Mex.

U. S . Atomic Energy Commission, Division of Biology and Medicine,

Washington, D . C .

September 1960

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ABSTRACT

Selected physical an d biological data bearing upon the environmental variations created bynuclear explosions are presented in simplified form. Emphasis is placed upon the "early" co nsequences of exposure to blast, thermal radiation, and ionizing radiation to elucidate the com

parative ranges of the major effects as they vary with explosive yield an d as they contribute tothe total hazard to man. A section containing brief definitions of the terminology employed isfollowed by a section that utilizes text an d tabular material to set forth events that follow nu

clear explosions and the varied responses of exposed physical an d biological materials.

Finally, selected quantitative weapons-effects data in graphic an d tabular form are presentedover a wide range of explosive yields to show the relative distances from Ground Zero affected

by significant levels of blast overpressures, thermal fluxes, an d initial an d residual penetrating ionizing radiations. However, only the "early" rather than the "late" effects of the latterare considered.

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FOREWORD

Following submission of the initial draft of this brochure to the Atomic Energy Commis

sion, the Civil Effects Test Operations of the Division of Biology an d Medicine, arranged for a

critical review by over 25 selected individuals, all knowledgeable in the field of weapons ef

fects. Although most of the reviewers recognized the preliminary nature of the work, pointed

out errors, and offered suggestions an d constructive criticism, they expressed considerable

interest in the presentation. This led to a collaborative effort between the Lovelace Foundation and the Civil Effects Test Operations to provide a corrected version of the first draft for

reproduction, which essentially comprises the material that follows. Major revisions of thedata are underway. Consequently, the present publication is regarded as an interim measure

to serve only until an expanded text of the work can be made available. Since nuclear effects is

a dynamic subject under continuous study, the reader can look to the future for the periodic

appearance of quantitative data that will refine the basic understanding of nuclear phenomenol

og y an d the response of exposed physical an d biological materials.A ll the information contained herein is from unclassified sources, including scientific

journals, text books, and Weapons Test Reports that docuinent studies made during full-scale

nuclear tests, many of which were carried ou t under the direction of the Civil Effects Test

Operations. Since great effort was made to keep the Weapons Test Reports unclassified and tonote bibliographic references, those interested can review the original publications. Too, much

of the quantitative weapons-effects data utilized were drawn from the very informative anduseful text The Effects ofNuclear Weapons, and the authors wish to acknowledge their indebt

edness to this work which was so competently edited an d prepared by Samuel Glasstone for the

Department of Defense an d published by the Atomic Energy Commission in June 1957. We arealso grateful to personnel of the Sandia Corporation, Albuquerque, N ew Mexico, wh o not onlycontributed suggestions regarding the data included on residual radiation, bu t lent their analyti

cal skill an d arranged machine computations from which all the fallout charts were drawn.

Clayton S. White, M.D.

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A C K N O W L E D G M E N T S

The authors wish to express their deep appreciation to members of the Staff of the Sandia

Corporation and the Lovelace Foundation wh o contributed computational, analytical, illustrative, editorial, and secretarial work that made this brochure possible.

Among the many individuals at Sandia Corporation with whom discussions were held, wewish particularly to express our thanks to Dr. W. W. Bledsoe, Mr. D . A. Young, Mr. M,

Cowan, and Mr. B. N. Charles for their critical suggestions and analytical help along with

timely machine computations.

Among the many persons at the Lovelace Foundation who contributed, we are especially

grateful for additional machine computations to Mr. R ay W. Albright, who, along with Mr.

Robert Ferret, Mr. Malcolm A. Osoff, Mr. E . Royce Fletcher, an d Mr. Jerome Kleinfeld,

also lent analytical aid. Mr. John L. Howarth aided in preparing some of the text dealing with

ionizing radiations.

The illustrative tasks, including graphs, the many fallout charts and photographic repro

ductions, were handled by Mr. Robert A. Smith, Mr. George A. Bevil, Mr. Edward M.

Johnsen, and Mrs. Holly Ferguson.

Editorial and secretarial duties fell to Mrs. Isabell D . Benton, who, aided by Mrs.

Barbara Kinsolving, typed the entire manuscript and spent many long hours checking the

tables, text, an d bibliographic references.Lastly, the Lovelace Foundation wishes to acknowledge the support of the Division of

Biology and Medicine of the U . S . Atomic Energy Commission and the Defense Atomic Support

Agency who have jointly funded the work in Blast Biology over the past year. The coordinatedunderstanding of both organizations has allowed perusal of work consonant with the interestsof each agency including completion of this text, compilation of which was begun in previousyears under contract with the Atomic Energy Commission.

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CONTEN TS

ABSTRACT...............FO R E WO R D...............ACKN O WLE DGM E N T S  .............IN TRODUCTIO N...............7TERMINOLOGY  AN D DEFINITIONS

...........9

Bursts............... 9Explosive Yield..............9Fission Yield...............9Blast Pressures..............9Thermal Radiation..............0Ionizing Radiation.............. 0

ORIENTATION...............2Physical Parameters.............2

Blast Effects.............. 2Pressure (Incident, Reflected, Dynamic) and Wind Velocity

..... 2

Pressure and Structures

...........2

Pressure and Missiles............2Pressure and Displacement of Man.........2Thermal Effects.............. 2

Ball of Fire...............2Emission..............2Attenuation..............2Shielding.............. 4Augmentation.............. 4Ignition Energies.......... . .24

Ignition Points for American Cities.........4Fire Storm

..............4

Ionizing-radiation Effects

............4

Initial Radiations .............4Neutrons..............4Gamma-rays.............4Emission.............. 4Attenuation ..............6Augmentation.............6Neutron-Gamma Ratios...........6Shielding..............6

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C O N T E N T S (Continued)

Residual Radiation............8Emission.............8

Decay...............2Attenuation..............2Shielding..............2

Biological Parameters.............2Blast Effects..............2

Primary (Pressure Effects)

...........2

Fast-rising Overpressures of Long Duration

.......5

Slowly Rising Overpressures of Long Duration.......5

Orbital Fracture............5Stepwise Fast-rising Overpressures of Long Duration . . . , .35

Fast-rising Overpressures of Short Duration.......7

Eardrums..............7Secondary (Missile) Effects...........7

Penetrating.............7Nonpenetrating.............0

Thermal Effects.............0Skin Burns..............0Extent of Burn and Mortality

...........0

Healing Time of Experimental Burns

.........0

Flash Blindness.............0Retinal Burns.............0lonizing-radiation Effects............4Acute Exposure.............4Chronic Exposure.............4Accumulative Genetic Effects..........4Emergency Exposure............4Hospitalization.............4

QUANTITATIVE WEAPONS-EFFECTS DATA.........7

Comparison of Blast, Thermal Radiation, and Ionizing ,Radiation

.....8

Tabular Weapons-effects Data for Selected Parameters . . . . . .48

Tabular Comparative Weapons-effects Data for Selected Parameters ...9

Graphic Scaled Ranges for 100-rem Initial Ionizing Radiation, 1-psi Blast Over

pressures, and Thermal Fluxes Required for Second-degree Burns as a

Function of Explosive Yield...........0Graphic Scaled Ranges for 30- and 100-rem Initial Ionizing Radiation, 1- and 5-psi

Blast Overpressures, and Thermal Fluxes for Second-degree Burns as a

Function of Explosive Yield (1 , 20, 100, and 1000 K t)......1

Graphic Scaled Ranges for 30- an d 100-rem Initial Ionizing Radiation, 1- and 5-psi

Blast Overpressures, and Thermal Fluxes for Second-degree Burns as a

Function of Explosive Yield ( 1 and 10 Mt) . . . . . . .52

Graphic Scaled Ranges for 30- and 100-rem Initial Ionizing Radiation, 1- and 5-psiBlast Overpressures, and Thermal Fluxes for Second-degree Burns as a

Function of Explosive Yield (20 Mt)

.........3

Graphic Expanded Plots of Scaled Ranges for 30- and 100-rem Initial Ionizing

Radiation, 1- and 5-psi Blast Overpressures, and Thermal Fluxes for Second-

degree Burns Applied to 1-kt Explosive Yield.......4

Graphic Expanded Plots of Scaled Ranges for 30- and 100-rem Initial Ionizing

Radiation, 1- and 5-psi Blast Overpressures, and Thermal Fluxes for Second-

degree Burns Applied to 20-kt Explosive Yield.......5

10

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CONTENTS (Continued)

Graphic Expanded Plots of Scaled Ranges for 30- and 100-rem Initial Ionizing

Radiation, 1- and 5-psi Blast Overpressures, and Thermal Fluxes for Second-

degree Burns Applied to 100-kt Explosive Yield.......5

Graphic Comparison of Yield-Range Relations for 1- and 5-psi Blast Over

pressures, 30- and 100-rem Initial Ionizing Radiation, and Thermal Fluxes

Required for Second-degree Burns.........7Tabular Comparison of Relations Between (a ) Residual Radiation and (b) Blast,

Thermal, and Initial Radiation Effects Within the Immediate Target Area, Giving

Ranges and Areas Measured Within the First-degree Burn Line for a 20-Mt

Surface Burst (5 0 per cent Fission Yield)........3Graphic Comparison of Range and Areas for Selected Weapons-effects ParametersWithin the Immediate Target Areas, Including Isodose-Rate Contours for Residual

Radiation A ll Estimated for a 20-Mt Surface Burst (5 0 per cent Fission

Yield)...............9Penetrating Residual Ionizing Radiation.........Q

Tabular Data Showing Dose Rate and Accumulated Dose as Functions of Time ( 1 Hr

to Infinity) and Various 1-hr Reference Dose Rates (3 0 to 3000 R/hr) 6 0

Computed Infinity Isodose Contours (100 and 1000 R ) for 20-Mt Surface Burst

(1 0 M t Fission Yield), Using Wind Patterns of Four Selected Days . . - 61

Computed Isodose-Rate Contours (100, 1000, and 10,000 R/hr) at H + * /4 and H + 2 Hrfor a 20-Mt Surface Burst (1 0 M t Fission Yield), Using Wind Pattern of M ay 12,

1956...............2Computed Isodose Contours (100, 400, 1000, an d 4000 R ) at H + 1 and H + 2 Hr for

a 20-Mt Surface Burst (1 0 Mt Fission Yield), Using Wind Pattern of M ay 12 ,

1956...............3Computed Infinity Isodose Contours (100, 400 , 1000, 3000, and 8000 R ) at Near

Ranges for 20-Mt Surface Burst (1 0 M t Fission Yield), Using Wind Pattern ofM ay 12, 1956..............4

Computed Isodose-Rate Contours (100 and 1000 R/hr at H + 2 Hr and 100, 1000, and

20 ,000 R/hr at H + % Hr) for a 20-Mt Surface Burst (1 0 M t Fission Yield), Using

Wind Pattern of Aug. 1, 1956...........5Computed Isodose Contours (100, 400 , 1000 , an d 5000 R ) at H + 1 and H + 2 Hr for a

20-Mt Surface Burst (1 0 M t Fission Yield), Using Wind Pattern of Aug. 1,

1956

...............6

Tabular Data Showing Computed Areas Included Within Isodose-Rate Contours

(100 to 20 ,000 R/hr) at H + V   and H + 2 Hr for a 20-Mt Surface Burst (1 0 M tFission Yield), Using Wind Data for Aug. 1, 1955, May 12, 1956, and Aug. 1,

1956...............7Tabular Data Showing Computed Areas Included Within Isodose Contours (100 to

20 ,000 R ) at Infinite Time and H + 2 and H + 1 Hr for 20-Mt Surface Burst

(10 Mt Fission Yield), Using Wind Patterns of Aug. 1, 1955, May 12, 1956,Aug. 1, 1956, and M ay 12, 1954..........7

Tabular Data Showing Computed Areas Included Within Isodose Contours (100 to

20,000 R ) at 1, 2, and 24 Hr, 1 Week, 1 Month, and Infinite Time for Surface

Bursts of 1, 20 , and 100 K t (100 per cent Fission Yield) and 1, 10, and 20 Mt(50 per cent Fission Yield), Assuming a 15-mph Wind at A ll Altitudes 68

Weighted Hodographs Showing General Directions of Fallout for Summer Seasons

from a 20-Mt Surface Burst (1 0 M t Fission Yield), Using Wind Data Sampled at

Random Bimonthly over Five Years.........9Weighted Hodographs Showing General Directions of Fallout for All Four Seasons

from a 20-Mt Surface Burst (1 0 M t Fission Yield), Using Wind Data Sampled at

Random Bimonthly over Five Years.........011

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I L L U S T R A T I O N S (Continued)

15 Infinity Isodose Contours for a 20-Mt Surface Burst Predicted for the WindPattern of M ay 12, 1956............4

16 Isodose-Rate Contours at Indicated Times for a 20-Mt Surface BurstPredicted for the Wind Pattern of Aug. 1, 1956 . . . . . . . . ,55

17 Isodose Contours for a 20-Mt Surface Burst Predicted for the Wind

Pattern of Aug. 1, 1956............g18 Directions of Fallout from a 20-Mt Surface Burst at Albuquerque forSummer Seasons Computed Using Wind Data Sampled Randomly

(Bimonthly over Five Years)

...........g

19 Direction of Fallout from a 20-Mt Surface Burst at Albuquerque

Computed Using Wind Data Sampled Randomly (Bimonthly over Five

Years)................020 Probabilities for Fallout Gamma Radiation from 1-Mt Burst (Summer Season) . . 71

21 Probabilities for Fallout Gamma Radiation from 1-Mt Burst (Winter Season) . . 72

22 Probabilities for Fallout Gamma Radiation from 20-Mt Burst (Summer

Season)...............323 Probabilities for Fallout Gamma Radiation from 20-Mt Burst (Winter Season) . . 74

24 Probabilities for Fallout Gamma Radiation from 20-Mt Burst (Spring Season) . . 75

25 Probabilities for Fallout Gamma Radiation from 20-Mt Burst (Fall Season) . . 73

26 Computed "Maximized" Isodose-Rate Contours for 20-Mt Burst

....7

27 Computed "Maximized" Isodose Contours for 20-Mt Burst

.....3

28 Computed "Maximized" Infinity Isodose Contours for 20-Mt Burst....9

29 Computed "Maximized" Infinity Isodose Contours for 20-Mt Burst 39

TABLES1 Calculated Wind-velocity Relations with Pressure Parameters (Sea Level) . . 23

2 Relation Between Overpressure an d Physical Damage.......33 Relation Between Overpressure and Missile Parameters......34 Blast Displacement of 165-lb Anthropometric Dummies......35 Thermal Energies Required to Ignite Houses an d Material . . . . . .25

6 Exterior Ignition Points in and near Surveyed American Cities . . . . .25

7 Percentage of Total Initial Gamma-radiation Dose Received at Ranges of 0.5

an d 1.5 Miles from 20-kt and 5-Mt Nuclear Detonations, Respectively, as aFunction of Time.............5

8 Approximate Relative Contributions of Neutrons an d Gamma Rays to the

Initial Radiation Expressed as Percentage of Total Biological Dose of600 an d 20 0 Rem for Different Explosive Yields.......7

9 Approximate Shielding Characteristics of Material Against Initial Gamma

Radiation Showing the Relation Between Shield Density and the Thickness

That Will Reduce the Radiation by One-half........710 Approximate Attenuation Factors for Initial Gamma Radiation as a

Function of Shield Thickness for Indicated Materials . . . . . .2911 Approximate Shield Thickness Required to Attenuate Neutron Radiation

by the Indicated Factors............912 Decay of Residual Gamma Radiation from an Explosion Having a 1-Mt

Fission Yield..............313 Seven-tenths Rule for Approximating Decay of Residual Gamma Radiation . . .33

14 Approximate Times of Fall of Various Sized Radioactive Particulates from80,000 Ft an d Distance Traveled in a 15-mile Wind (a t All Altitudes) asRelated to Proportion of Initial Gamma Activity at Altitude and at Sur

face Corrected for Decay During Transport........313

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TABLES (Continued)

15 Approximate Attenuation of Residual Gamma (0.7 Mev) Radiation with

Distance Above Earth's Surface..........416 Shielding Factors for Typical Light Residential Structures Against Gamma

Rays Simulating Penetrating Residual Radiation.......417 Approximate Attenuation Factors for Gamma Rays from Fission Products

as a Function of Shield Thickness for Indicated Materials . . . . .34

18 Shock-tube Mortality Data for Fast-rising Long-duration OverpressuresWhen Incident an d Reflected Pressures are Applied Almost Simultane

ously

...............6

19 Exposure to Slow-rising Overpressures of Long Duration . . . . . - 36

20 Orbital Fracture in Dogs Exposed to Slow-rising Long-duration Overpressures . . 36

21 Mortality Data for Guinea Pigs Exposed Against, and at Various Distances

from, the E nd Plate Closing a Shock Tube to Fast-rising Long-duration

Overpressures When the Incident an d Reflected Overpressures areApplied in Two Steps............3

22 Fast-rising Short-duration Overpressures Required for Near 100 Per Cent

Mortality in Dogs.............323 Relation Between Overpressure an d 50 Per Cent Mortality for Animals Exposed

to Single Sharp-rising Overpressures of Indicated Durations . . . . .33

24 Pressure Tolerance of the Eardrums of D og and M an . . . . . . -39

25 Velocity-Mass Probability Relationships Required for Small Window-glass

Fragments to Traverse the Abdominal Wall and Reach the Peritoneal

Cavity of Dogs..............926 Effects of Missiles on Human Cadavers.........927 Impact Velocity Required for Puncturing Rabbit Eyeball Embedded in Gelatin . . 39

28 Effects of Missile Impact on the Chest and Head........129 Velocities of Impact Against a Hard Surface Associated with 50 Per Cent

Mortality of the Indicated Species of Animals with Extrapolation to M an . . .41

30 Approximate Impact Velocities and Equivalent Heights of Drop for Fractureof Human Sjpine, Skull, Feet, and Ankles.........1

31 Thermal Energies for Burns of Bare White Skin........232 Comparison of Thermal Energies Applied over 54 0 Msec Required for Burns

of the Skin of White and Negro Volunteers

........2

33 Mortality in Treated Burn Cases Related to Percentage of Body Area Burned . . 42

34 Estimated Relative Importance of Concomitant Second- an d Third-degree

Burns Associated with an Average Mortality of 50 Per Cent in Treated Cases . . 43

35 Estimated Healing Time for First-, Second-, and Third-degree Burns and

Simplified Clinical Comments...........336 Probable Effects in Humans of Acute Exposure to Ionizing Radiation Over

the Whole Body..............337 Estimate of Effective Dose and Lethality of Various Dose Rates to M an . . .45

38 Estimated Doses for Varying Degrees of Injury to M an . . . . . .45

39 Estimated Clinical Course and Hospitalization Requirements for Humans

Exposed to Various Acute Doses of Penetrating Radiation . . . . -45

40 Weapons-effects Data for Selected Parameters

........8

41 Comparative Weapons-effects Data

..........9

42 Comparative Effects Data for a 20-Mt Surface Burst (1 0 M t Fission Yield) . . .58

43 Accumulated Radiation Dose and Dose Rate as a Function of the 1-hr Reference

Dose Rate and Time after Detonation.........044 Areas (in Square Miles) Enclosed Within Specified Isodose-Rate Contours

Computed for Penetrating Fallout Radiation and Unshielded Conditions

from a 20-Mt Surface Burst (1 0 Mt Fission Yield) at Albuquerque Using

Wind Patterns of Indicated Dates..........714

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TABLES (Continued)

45 Areas (in Square Miles) Included Within Specified Isodose Contours Computed

for Penetrating Fallout Radiation and Unshielded Conditions from a 20-Mt

Surface Burst (1 0 Mt Fission Yield) at Albuquerque Using Wind Patterns of

Indicated Dates.............746 Computed Areas for Penetrating Fallout Radiation Inside Indicated Isodose

Contours at Specified Times After Detonation for Various Explosive

Yields

...............8

15

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INTRODUCTION

The advent of nuclear weapons and their integration into programs vital to national defenseemphasize the need for broad public knowledge of nuclear effects. Also, the increasing employ

ment of nuclear materials in an expanding variety of peaceful applications serves notice that

the public must learn to live in a nuclear age. Regardless of whether the future holds continued

peace or the necessity of surviving a national emergency involving nuclear war, each individual

citizen should share with the Government the responsibility of providing sensible levels of pro

tection against nuclear effects.

The purpose of this publication is to provide citizens and Government alike with a singlesimplified source of information about nuclear weapons and related biological data which deals

in a comparative way with effects du e to blast and to thermal and ionizing radiations. Such data

will help the average man assess for himself the risks he an d his family face in the nuclear

era and will provide background information for decisions and action regarding protective co nstruction.

Accordingly, in the material that follows selected weapons-effects data have been assembled for quick reference to aid those interested in the physical and biological effects of nuclear

weapons. The quantitative data are preceded by two sections chosen to facilitate orientation ofthe reader. The first section contains brief definitions of the terminology employed throughout

the brochure. The second section deals grossly with the physical and biological consequences

of the several environmental variations created by nuclear explosions. Such information will

foster appreciation of the comparative ranges for the major effects as these vary with explo

sive yield an d as these contribute to the total hazard to man.It is well to point ou t here that the values for an y given effect can vary considerably de

pending on many factors, not the least of which are weapon design and yield, location of burst,

weather, terrain, and range from the detonation. Even though the numbers chosen are the out

come of experimental, theoretical, and full-scale studies in which many uncertainties were

appreciated, they nevertheless represent best approximations an d are reasonably valid for the

purposes of orientation an d planning. However, it should be pointed ou t that the figures for

overpressure are thought to be reliable within 20 per cent; those for thermal radiation within

a factor of 2; an d those for initial ionizing radiation within factors of 2 and 10 for the lower an dhigher explosive yields, respectively.

17

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TERMINOLOGY AN D DEFINITIONS

Bursts

S U R F A CE BURSTS : Bursts on or above the surface at heights that involve contact between the

fireball an d the surface of the earth.

TYPICAL Am B U R S T S : Air bursts in which there is no contact between the fireball and surface of earth an d in which the heights are such as to produce maximal blast damage to

an average city.

Explosive Yield

KILOTON (kt): A unit of explosive yield for a nuclear explosion; it is equivalent in energy to

the energy released by the detonation of 1000 tons of TNT.MEGATON (Mt): A unit of explosive yield equivalent in energy to 1000 kt, or 1,000,000 tons, of

T N T .

Fission Yield

FISSION Y IE L D: That portion of the total explosive yield of a nuclear explosion attributable to

nuclear fission. The units are kilotons andmegatons. Megatons of fission yield are to

be distinguished from megatons of total yield.

Blast Pressures

O V E R P R E S S U R E : The transient pressure variation above the ambient produced by an explosion;

it travels radially from the source of the detonation.

LOCAL-STATIC OR I N C I D E N T PRESSURE: The overpressure measured side-on to the ad

vancing front of an explosive-produced overpressure.

REFLECTED P R E S S U R E : The instantaneous pressure that occurs when a pressure frontstrikes a surface.

D Y N A M I C P R E S S U R E (Q): The difference between the pressures measured head-on an d side-on to an advancing pressure pulse associated with an explosion. Thus Q , or dynamic

pressure, is a measure of the force exerted by the blast winds. Hurricane wind velocities by definition are 75 mph or greater.

P O U N D S PER S Q U A R E I N C H (psi): A unit used to express the force exerted by blast-produced

pressures.MAXIMAL O V E R P R E S S U R E (Pmax< ): The maximal overpressure existing at any location due

to an explosion. This may refer to incident or reflected pressures.P R I M A R Y , S E C O N D A R Y , AN D T E R T I A R Y B L A S T EFFECTS: Primary, secondary, and terti

ary blast effects are biologically those due, respectively, to (1 ) pressure variations perse, (2 ) the impact of penetrating or nonpenetrating missiles energized by the blast, and

(3 ) the physical displacement of a target by blast winds (may be damaging during the ac-celerative or decelerative phase of the experience).

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R E L A T I V E BIOLOGICAL EFFECTIVENESS (RBE)*t: A n expression used to compare the

biological effectiveness of different kinds of ionizing radiation,

HAD : A unit of absorbed dose (1 rad = 10 0 ergs/g).R O E N T G E N E Q U I V A L E N T MAN (rem)*t: The unit of the R BE dose; it is equal to the radiation

dose in rads multiplied by an appropriate RBE.t [Note: Although there are very real

distinctions between exposure dose (r), absorbed dose (rads), and biologically effective

dose (rem), the roentgen and rad units are, numerically speaking, no t too different.

Neither does the rem value for X or gamma radiation numerically vary much from those

expressed in roentgen or rad units since the R BE by definition is approximately 1. Once

the absorbed dose (in rads) for neutrons is converted to rem, using an appropriate RBE,the numerical value represents a gamma equivalent of the neutron dose. Consequently,

for practical purposes, the reader may regard the rem values noted in future sections

of the brochure as roughly equivalent numerically to the exposure dose in roentgens.

Although, strictly speaking, this is technically incorrect, the errors involved in such an

approximation are generally much smaller than the other sources of uncertainty and

seem acceptable on this basis.]

EFFECTIVE BIOLOGICAL D O S E (EBD) : This is the accumulated exposure dose of radiation

corrected for biologic recovery and repair that has occurred at a particular and speci

fied time after exposure. Some consider radiation injury as approximately 90 and 10 per

cent reparable and irreparable, respectively, with the former being accomplished in

about three months, but nearly 50 per cent complete in on e month, t Recognizing the E BD

will allow a more refined prediction of medical and biological effects of radiation and

the recovery therefrom.EFFECTIVE A CCU M U L A T E D DOSE (EAD) : The accumulated exposure dose of radiation cor

rected by a factor proportional to the E BD as appropriate to the time in question.

Taken from £ / . S . Bureau of Standards Handbook 62 , 19 56 , 4 8 to which the reader is referred for more precise definitions and explanations. Also see Radiological Health Handbook,

U. S . Department of Health, Education and Welfare, 1957. 2 8tFor the data given later covering initial radiations, the rem values were computed using

an R BE for bomb neutrons of 1.7, as was done in The Effects ofNuclear Weapons.2 4{See National Council on Radiation Protection Subcommittee 14 Handbook, Exposure to

Radiation in an Emergency. 4 9

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Table 1 ALCULATED WIND-VELOCITY RELATIONS WITH PRESSURE PARAMETERS (SEA LEVEL)*

Maximum pressure,

Incident

1

2

5

10

Reflected

2

4

11

25

psi

Dynamict

0.02

0.10.6

2

Wind

velocity,

mph

40

70

160

290

Maximum pressure,

Incident

20

30

50

100

Reflected

60100

200

500

psi

Dynamict

8

16

40

12 5

Wind

velocity,

mph

500670

940

1400

*Data computed from

tA hurricane wind of 12 0 mph exerts a dynamic pressure of about 0.25 psi.

Table 2 ELATION BETWEEN OVERPRESSURE AND PHYSICAL DAMAGE*

Type of

structural material

Glass:

Window

Plate

Houses:Wooden

Brick

Apartments,  brick

Over

pressure,

psi

0,1

0.02

1*2

4-5

54-5

5-7

Physical effects

Damage

Damage to large

glazed areas

50 per cent damaged

Destroyed

Destroyed

Moderate damage

Severe damage

Type of

structural material

Reinforced concrete

Frame buildings

Wall-bearing massive

buildings

Motor vehicles

Parked aircraft

Over

pressure,

psi

4-6

6-8

6-8

8-10

2-3

10-15

1-3

4-6

Physical effects

Moderage damage

Severe damage

Moderate damage

Severe damage

Light damageSevere damage

Minor to major

repair  required

Unusable to de

stroyed

*Selected from  SCTM 195-58(51). 4 1

Table 3 ELATION BETWEEN OVERPRESSURE AND MISSILE PARAMETERS*

Max.

pressure,

psi

1.9

3.85 .0

8.515.017.317.3

Type of

missile

Window glass

Window  glass

Window  glass

Natural stones

Natural stones

Natural stones

Irregular steel

objects

Velocity,

Geometric

mean

108

168170

2 75

692

43 2

2 40

ft/sec

Range

50-178

60-310

50-400

167-413

379-1100

300-843

195-301

Mass,

Geometric

mean

1.45

0.58

0.13 0

0.23 0

0.50 0

0.21 0

34.5

g

Range

0.03-10 

0,01-10

.002-140

.038-22.2

.043-8.82

.010-13.4

9.0-86.0

Max. missile

density,

missiles/sq ft

0.4

15 9

388

35

4.7

99 .1

3.6

'Reports  WT-1168, 5 AECU-3350, 6 and TID-5564. 4 4

Table 4 BLAST DISPLACEMENT OF 165-LB ANTHROPOMETRIC DUMMIES*

Max.

pressure,

psi

5.3

6.6

Max.

Q ,psi

0.7

15.8

Initial

dummy

position

Standing

Prone

Standing

Prone

Max. horizontal

velocity,

ft/sec

21.0

0

Not known

Not known

Time to max.

velocity,

sec

0.5

Not known

Not known

Displacement,

ft

21.9 dow nwind

None

2 5 6 downwind,

44 to right

12 4 downwind,

2 0  to right

*Report WT-1469.4

2 3

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Table 5 HERMAL ENERGIES REQUIRED TOIGNITE HOUSE S A ND MATERIAL*

Material

Ignition energy, cal/cm2

20 kt 10 M t

Wooden houses:

Weathered

Freshly painted white

Newspaper

Wool flannel, black

Cotton shirting, tan

Cotton auto seat covers, green,

brown, white

Rayon taffeta, wine

Fine kindling fuels

Fine grass

1 2

25

3

8

7

9

2

5

5

6

1 6

1 3

1 6

3

7

1 0

*Selected from

Table 6 EXTERIOR IG NITION POINTS IN A ND NEAR SURVEYED AMERICAN CITIES*

Classification of area

Wholesale distribution

Slum residential

Neighborhood retail

Poor residential

Approx. No.

ignition points

per acre

27

20

1 1

9

Classification of area

Small manufacturing

Downtown retail

Good residential

Large manufacturing

Approx. No,

ignition points

per acre

7

4

3

3

*Selected from 24

Table 7 PERCENTAGE OF TOTAL INITIAL GAMMA-RADIATION DO SE RECEIVED AT

RANGES OF 0.5 A N D 1.5 MILES FROM 20-KT A N D 5-MT NUCLEAR DETONATIONS,RESPECTIVELY, AS A FUNCTION OF TIME*

Percentage of

Explosive

yield

20 kt

5   M t

Range,

miles

0.5

1.5

initial gamma-radiation dose

delivered at indicated times

1 sec

67

5

2 sec

78

1 7

4 sec

88

43

7 sec

95

76

1 0 sec

97

90

15 sec

1 00

98

20 sec

1 00

1 00

* Selected from 2 4

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remainder of the initial gamma radiation is given off by the rising fireball an d radio

active cloud.The initial ionizing radiation moves away from the source at speeds equal to,

an d somewhat less than, the speed of light for the gamma rays an d neutrons, respec

tively. This radiation undergoes attenuation with distance for a number of reasons, the

most important being (1 ) the greater area over which the radiation is spread with increasing range; (2 ) absorption by air, which is generally less effective for high than for

low energy radiation an d more effective for neutrons than for gamma rays; and (3 )

scatter by air molecules and other material contained in the atmosphere. Appreciation

of the comparative attenuation of the initial neutrons and gamma rays by air is given bya quantity known as the "relaxation length" of the radiation, which is that distance required to reduce the radiation dose by a factor of e (= 2.7183) , the base of the natural

logarithms. The relaxation length is dependent upon the air density (and hence the mass

of material traversed by the radiation) an d the energy and kind of radiation involved.

A t sea level an d for initial bomb radiation, the relaxation length is 338 yards (1014 ft)for gamma and 24 2 yards (726 ft) for neutron radiations. A consequence of this fact isthat neutron dose decreases more rapidly with increasing range than does the gamma

dose, and at the greater ranges only gamma rays contribute significantly to the hazard

from initial radiation.

Three factors contribute to increase the radiation exposure of a given targetduring the first minute after a nuclear explosion above the dosage du e to radiations com

ing from the fissioning material, the fireball, an d the nuclear cloud. These are: (1 )

scatter of radiation from materials, including air, close to the target; (2 ) activation orexcitation of materials in the vicinity of the target by neutrons, particularly the nitrogen

contained in the atmosphere and elements in soil and structures; and (3 ) a decrease in

air .density associated with the negative phase of the blast pressures, which results in

less attenuation of the gamma radiation by air and which is particularly effective in in

creasing the range of gamma rays for the larger yield explosions; i.e., the relaxation

length applicable to gamma rays increases with lower air density and hence attenuation

by the atmosphere decreases.

The relative contribution of neutrons and gamma rays to the initial

radiation is sensitive to the design and yield of the nuclear device, to range, and to fac

tors that contribute to attenuation and augmentation of the radiation. Some appreciation

of the interplay of all these intangibles as they control the percentage of neutron an d

gamma dose is shown in Table 8 , which gives the approximate neutron and gamma portions of the hazard as these vary with explosive yield. The ranges used for each yield

are those in which the radiation would be 600 an d 20 0 rem. The yields for which the

gamma and neutrons would each contribute 50 per cent of the total biological dose of

200 and 600 rem would be near 15 and 30 kt, respectively. Table 8 shows that for

yields less than these the neutrons contribute more of the dose than do the gamma rays.The reverse is true for the higher yields. Likewise, for higher doses than those shown,and therefore at lesser ranges, the neutron contribution would be greater than listed inTable 8 . There are, of course, uncertainties with regard to Tables 7 and 8 which con

cern fission-fusion ratios for a given explosion because as the fission portion of the

total yield decreases, so does the delayed gamma-ray contribution to the initial radia

tion that arises mostly from fission products in the fireball, stem, and cloud. To the

contrary, the neutron an d prompt-gamma contributions to the initial radiation will in

crease.Shielding from penetrating initial radiation arising from a nuclear explosion in

volves many complexities, not the least of which concern differences between neutrons

and gamma rays, the wide energy range of each, and variations associated with shield

thickness and materials* However, certain practical generalizations are useful. Forexample, the reduction of gamma radiation is related to the density of material through

which the radiation passes, as illustrated in Table 9, which notes the thickness of mate

rials of specified density that attenuate the radiation by a factor of 2. The reader will

note that the product of the density of the shield an d the half-value layer is about equal

to 800 . Thus, if the density (x) in pounds per cubic foot of a potential shield is known,

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Table 8 APPROXIMATE RELATIVE CONTRIBUTIONS OF NEUTRONS AND GA MMA RA YS

TO THE INITIAL RADIATION EXPRESSED  AS PERCENTAGE OF TOTAL BIOLOGICAL

DOSE OF 600 AN D 200 REM FOR DIFFERENT EXPLOSIVE YIELDS*

Total

biologic 

dose,

rem

200

600

Kind of

radiation

Neutrons

Gamma

Neutrons

Gamma

Approximate percentage contributions of gamma rays and neutrons

to the initial radiation for indicated yields

1 kt

70

30

62

38

20   kt

48

52

57

43

1 00   kt

30

70

38

62

500 kt

5

95

7

93

1 Mt

2

98

3

97

5 Mt

-0

-100

199

20 Mt

-0

-100

~0

-100

NOTE: The levels of exposure chosen "fixed" the range for each yield; e.g., the ranges were

those which resulted in a total biologic dose of 20 0 and 60 0 rem. 

*Selected from

Table 9 APPROXIMATE SHIELDING CHARACTERISTICS OF

MATERIAL AGAINST  INITIAL GA MM A RADIATION SHOWIN G THE

RELATION BETWEEN SHIELD DENSITY A ND THE THICKNESS

THAT WILL REDUCE THE RADIATION BY ONE-HALF*

Materials

Lead

Steel

Concrete

Earth

Water

Wood

Density,

Ib/cu ft

70 7

490

144

1 00

62.4

34

Half-value thickness,

in.

0.6

1.5

6.0

7.5

13.0

23.0

Product

735

864

750

811

782

NOTE: Assumes 4.0 Mev  is an adequate  representation of the en

ergy of initial gamma radiation and  incorporates build-up factors

correcting for thick shields and broad radiation beams  (see pages

353 to 360 and 374 to 380,

*From 

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its half-value thickness can be estimated by dividing 800 by this number; i.e., 800/x =

half layer thickness in inches. Also, through the use of numbers close to those in Table

9 , it is possible to compute the thickness of materials that will attenuate initial gamma

radiation by different amounts. A s a convenience, Table 10 shows such data for quick

reference.

Also of interest are recent studies of Ritchie and Hurst 3 3 noting the shielding from

initial gamma radiation provided by light-frame houses. Such data incorporate the angular distribution of radiation which occurs under full-scale nuclear conditions. Figure 1

shows gamma attenuation as a function of penetration distance for tw o identical houses

measured in opposite orientations with dosimeters placed 42 and 84 in . above the floor.Similar data from the same authors 3 3 are presented in Fig. 2, which gives the attenua

tion values for initial neutron radiation as a function of house-penetration distance. Al

though the shielding afforded by houses may reduce the neutron dose by as much as a

factor of 2, the attenuation is appreciably less than this for gamma rays. In any case,

the shielding potential of houses against bomb radiations is small, but, at certain com

binations of range an d yield, it could be critical in reducing radiation fatalities.

In general, shielding against neutrons is much more complex than shielding against

initial gamma rays, and there is no straightforward correlation between attenuation an dthe density of material as applies with good approximation to gamma radiation. A n ade

quate shield must not only attenuate fast neutrons, but must also capture the slowed-

down neutrons and absorb any radiation that accompanies the capturing process. Boron

or boron-containing minerals, such as colemanite, are useful as absorbers of thermal

neutrons, the process being accompanied by the emission of low-energy gamma rays(0 .48 Mev). Since the latter are not difficult to attenuate, the inclusion of boron has advantages in shielding against neutrons an d will significantly reduce the induced radiation

on surfaces covered with colemanite or in boron-containing materials such as concrete. 2 4

Table 11 shows the thickness of different types of concrete which will reduce neutron

radiation by a factor of 2, i.e., the half-value thickness, and by factors varying from 10

to 100,000.

RESIDUAL RADIATION

The residual ionizing radiation, that occurring subsequent to 1 min following a nuclear ex

plosion, arises mainly from bomb residues including fission products, activated bomb

and other debris, and unfissioned uranium or plutonium. Although beta and alpha particles form a significant portion of the residual radiation, the present discussion will

be limited to gamma rays, the penetrating portion of the residual radiation.Penetrating gamma radiation from radioactive material in the rising fireball,

stem, and cloud is emitted "continuously" as it is when there is induced radiation in

soil, water, structures, and other materials. In case of an explosion in air wherein the

fireball makes no contact with the earth, the hazardous materials, as small particu-lates and gases, are carried to altitude and subsequently either fall back to the earthas dictated by gravity and the winds aloft in time periods like minutes, hours, and days

(early fallout) or are carried to the higher reaches of the atmosphere to undergo non-

uniform world-wide distribution and eventual deposit on the earth's surface in periodslike weeks, months, and many years (delayed fallout). The larger the yield, the higher

the fireball, stem, and cloud are carried and the more likely is fallout to be a delayed

as well as an early problem.

Surface or near-surface explosions carry tons of material, some of it radioactive byneutron activation, up into the stem and cloud where it is mixed and condensed with fis

sion products and bomb debris. This mixture also either falls back to earth in the

shorter time periods or reaches altitudes wherein world-wide distribution occurs, depending much upon explosive yield. However, the surface burst tends to maximize the

early fallout problem with which the subsequent text will deal.

The amount of radioactive debris formed in a nuclear explosion is mostly a function

of fission yield rather than total explosive yield, although neutrons from fusion reac

tions add to the induced radioactivity. Too, the induced components of the penetratingresidual radiation are sensitive to the character of the materials exposed in the vicinity

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Table 10 PPROXIMATE ATTENUATION FACTORS FOR INITIAL G A M M A RADIATION

A S A FUNCTION OF SHIELD THICKNESS FOR INDICATED MATERIALS*

Shield thickness for the

Attenuation

factor

2

4

10

50

100

1,000

10,000

100,000

Lead

(710 Ib/cu ft)

0,6

1.3

2.2

3.6

4.3

6.3

8.2

9.9

Iron and steel

(490 Ib/cu ft)

1.3

2.6

4.3

7.3

8.5

12

16

19

Concrete

(144 Ib/cu ft)

5.5

11

18

30

3 5

52

68

8 4

indicated materials, in.

Earth

( 100 Ib/cu ft)

8

16

26

43.

51

73

93

112

Water

(62.4 Ib/cu ft)

12

25

42

70

8 3

124

168

203

Wood (Fir)

(3.4 Ib/cu ft)

22

44

73

123

145

216

291

396

*From . 2 4

Table 11 APPROXIMATE SHIELD THICKNESS REQUIRED TO ATTENUATE

NEUTRON RADIATION BY THE INDICATED FACTORS

Type of

concrete or

aggregate

Ordinary*

Ordinaryf

Ordinary

Ordinary!

Ordinary +1.25% Pyrex

Magnetite

Limonite

Limonite +

scrap iron

Limonite +

scrap iron +

0.7% Pyrex

Concrete

density,

Ib/cu ft

144

143.3

146.7

149.8

149.2

236.0

164,2

275.5

224.7

Concrete thickness to reduce neutron radiation by

indicated factors, in.

2 10 100 1,000 10,000 100,000

3

2.2

4.2J

3.5

2.9t

3.3{

l.W

2.2J

2.Of

10

7.3

14

12

9.6

11

6.3

7.4

6.6

20

15

28

23

19

22

13

15

13

3 0

22

52

3 5

29

33

19

22

20

40

29

64

47

3 8

44

25

30

26

50

37

70

58

48

55

32

37

59

*Data from Glasstone 2 4 for bomb neutrons.

tData from Blizard and Miller4 for thermal neutrons.

tHalf-value thickness (attenuation by a factor of 2) from Callan 1 0 for thermal neutrons.

Other data calculated,

§Data from Price et al. 2 9 for fast neutrons.

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UJ

ocr

UJ

e n

C O

O

a

1.0

0.9

0.8 

0.7

0.6

S 0.5

L U

Qe n

0.4

0.3

HOUSE

42" STATION

84 "STATION

HOUSE 2

o

O

i I I8  12 16 20

HOUSE PENETRATION DISTANCE (FEET)

24 28

Fig. 1 Attenuation of gamma radiation by typical single-story Japanese houses.

(Data  from Ritchie and Hurst. 3 3 )

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10

0.9—

0.8LU

V)

§ 0.7 

c

0.6

V):D  oX

L U

ge n

0.5

oQ

0.4

HOUSE 1 HOUSE  2

42" STATION •

84" STATION •o

O

0.3 I I I I I I8 12 16  20

HOUSE PENETRATION DISTANCE (FEET)

24 28

Fig. 2 Attenuation of  fast neutrons by typical single-story Japanese houses.

(Data from Ritchie and Hurst. 3 3 )

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of an explosion; e.g., some elements when made radioactive remain so for long periods

of time, others only for short periods.

Fortunately, the intensity of the residual nuclear radiation decreases with time after

an explosion, as shown by Table 12, which indicates that only about 2 and 0.2 per cent of

the gamma radiation at 1 hr remain 1 day an d 1 week, respectively, after the detonation.

For general applications, the seven-tenths rule is useful in making rapid approximations

of the decay with time of a known level of residual gamma radiation measured at a par

ticular time. The rule states that as time increases by a factor of 7, the gamma-ray in

tensity decreases by a factor of 10. The application of this simple relationship is illus

trated in Table 13 .Besides radiation decay there are other factors that tend to decrease the resid

ual radiation reaching, or existing at, a given surface area. The first is the height of

the cloud and stem, which is mostly yield dependent. The second is the particle size ofthe fallout debris* The third is the winds aloft, and the fourth is weathering and leach

ing of the soil by wind and rain, which tends to spread the radioactive material furtheror to carry it into subsurface layers of the soiL The first three factors bear upon the

time of fallout arrival and the total surface area over which it is spread. Both a delay

in arrival and an increase in area decrease the level of contamination. Table 14 illus

trates these facts by giving the particle-size distribution of material in an atomic cloud

at an altitude of 80 ,000 ft; their time of fall to the earth's surface; the distance travelled

by particulates of selected size groupings during this period, assuming a 15-mph wind at

all altitudes; and the average radiation of selected size groupings expressed as a per

centage of the initial activity in the cloud right after the burst and when the particleswould arrive at the surface of the earth, allowance being made for decay during transport through the atmosphere. Consider the radiation contained in the 15 0 to 75/jt group

of particles to average about 18 per cent of the total activity just after the burst. Subse

quently, decay occurs during transport to and from an altitude of 80,000 ft . In coming

down, the particles would be transported 59 to 240 miles for the larger and smaller par

ticles, respectively, taking from about 4 to 16 hr. The average activity in this range ofparticle sizes would have decayed to near 0.015 per cent of the initial dose rate by the

time the particles reached the surface of the earth.Once the penetrating radiation is on the ground, a "flat" radioactive surface is

formed, and attenuation with distance above the surface is not straightforward, first,because radiation is received from below and laterally at all angles and, second, be

cause the radiation is scattered from the air molecules, the so-called "sky-shine."Practically, doses received at increasing distances above the surface do not fall of fvery rapidly, as Table 15 shows; e.g., at 20, 150, and 500 ft the radiation has decreased

by factors of about 2, 3, and 10, respectively.

The above information bears somewhat upon shielding provided by above-ground

structures against radiation from a uniformly contaminated plane. The problem is com

plicated by (1 ) the redistribution of source material due to the presence of the structure-material on the roof rather than the ground-and (2 ) the attenuation of radiatiqn due to

structural materials and the contents of the building. However, Table 16 sets forth ap

proximate protection factors that can be expected from shielding by light-frame structures against simulated penetrating fallout radiation. The table also notes that a sheltercovered by 3 ft of earth will give a shielding factor of 1000 or more against radiation

from fallout. Table 17 presents shielding data for various materials showing the attenu

ation factors for penetrating residual radiations. Since the latter have energies averaging less than those of the initial gamma radiation, shielding is less difficult, and the

reader should not confuse the attenuation factors for initial gamma radiation given in

Table 10 with those for fallout gamma rays set forth in Table 17 .

Biological Parameters

BLAST EFFECTS

It is now known that the tolerance of mammals (if the ear

drums and sinuses are ignored) to variations in environmental pressure depends a great

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Table 12 DECAY OF RESIDUAL GAMMA RADIATION

FROM AN EXPLOSION HAVING A 1-MT FISSION YIELD*

Time after

explosion

1 hour

1 day 1 week

1 month

1 year

Activity,

megacuries

300,000

6,600

64 0

110

5,5

Activity,

%

10 0

2.2

0.213

0.037

0.0018

*Data from

Table 13   SEVEN-TENTHS RULE FOR APPROXIMATING DECAY

OF RESIDUAL GAMMA RADIATION*

Time after burst

Hr

1

7

49

343

2401

days

0.04

0.29

2.04

14.3

100

Time factor

1

7

? 2

? 3

7 4

Dose rate,

r/hr

1000

10 0

10

1

0.1

Dose-rate

factor

1

1/10

1/100

1/1000

1/10,000

NOTE: These data are based upon the formula generally used;

i.e., R t = Rjt"1 ' 2 , where Rt is the dose rate at some instant and R t

is a later dose rate after an interval of time, t, has passed. This 

relationship is not strictly applicable to very early or very late

times after a burst, nor does  it apply to a given location on the

earth's surface until fallout is complete.

*Data from

Table 14 APPROXIMATE TIMES OF FALL OF VARIOUS SIZED RADIOACTIVE PARTICULATES

FROM 80,000 FT AND DISTANCE TRAVELED IN A 15-MILE WIND (AT ALL ALTITUDES) AS

RELATED TO PROPORTION OF INITIAL GAMMA ACTIVITY AT ALTITUDE AND AT SURFACE

CORRECTED FOR DECAY DURING TRANSPORT*

Particle

diameter,

M>340

340-250

250-150150-75

75-33

33-1616-8

8-5

Time

of fall,

hr

Up to 0.75

0.75-1.4

1.4-3.93.9-16

16-80

80-340

340-1400

1400-3400

Distance

traveled in

15-mph wind, miles

Up to 11

11-21

21-5959-240

240-1200

1,200-5,100

5,100-21,000

21,000-51,000

Percentage

of initial

activity

3.8

12,6

14.518.1

Percentage of

initial activity

deposited

0.0394

0.0964

0.04600.0154

*Data from

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Table  15 PPROXIMATE ATTENUATION OF RESIDUAL G AM M A

(0.7 M E V ) RADIATION W ITH DISTANCE ABOVE EARTH'S SU RFACE*

Distance above

ground, ft

20

150

30 0

Attenuation

factor

2

3

5

Distance above

ground, ft

50 0

1000

2000

Attenuation

factor

10

30

30 0

NOTE: Theattenuation factors

apply to 0.7-Mev gammarays,

which

simulates reasonably well a surface covered with fission products,

*Data from

Table 16 SHIELDING FACTORS FOR TYPICAL LIGHT RESIDENTIAL STRUCTURES

AG AINST GAMMA RAYS SIMULATING PENETRATING RESIDUAL RADIATION

Reduction factors*

Structure

Two-story wood-frame houset

One -story woo d ramblert

Two-story brick veneer!

Shelter (earth covered)

3 ft below gradett

Location

2nd floor, center

1st floor, center

Basement, center

Basement, corner

Basement, corner shelter

1st floor, center

1st floor, center

Basement, center

Roof con

tribution

0.076

0.034

0.015

0.10

0.034

0.015

Ground con

tribution

0.500.57

0.028

0,54

0,14

0.021

Total

0.58

0.60

0.043

0.64

0.17

0.036

Protection

factorf

1.71 .7

23§

4 0 1 T

< 1 0 0 1 T

1 .66**

28 §

1000 or

more

*Reduction factor represents the dose rate at a specified location divided by the dose rate outside at 3 ft

above ground.

tProtection factor represents the outside dose rate at 3 ft above ground divided by the dose rate inside

at the specified location.

tAfter Eisenhauer. 1 8 '

§ Applies to basement with no exposed walls.

fAfter Auxier; 1 Auxier, Buchanan, Eisenhauer, and Menker;2 and Strickler and Auxier.3 9

**Applies only for detector locations below window sill.

ttFrom

Table 17 APPROXIMATE ATTENUATION FACTORS FOR GAMMA RAYS FR OM FISSION

PRODUCTS AS A FU NC TIO N OF SHIELD THICKNESS FOR IN DICATED M ATERIALS*

Attenuation

factor

2

4

10

50

100

1,000

10,000

100,000

Lead

(710 Ib/cu ft)

0.28

0.64

1 ,0

1 .6

1 .9

2.73.5

4.3

Shield

Iron and steel

(490 Ib/cu ft)

0.7

1.8

2.7

4.2

4.8

6.8

8.8

11

thickness for indicated materials, in.

Concrete

(144 Ib/cu ft)

2.56.6

9. 7

14

16

22

27

32

Earth

(1 00 Ib/cu ft)

3.5

8.9

13

20

23

32

39

46

Water

(62.4 Ib/cu ft)

4.8

13

19

29

33

4 556

70

Wood (Fir)

(3.4 Ib/cu ft)

9.2

25

36

55

62

88

1 10

140

*Data from

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Table 18 SHOCK-TUBE MORTALITY DATA FOR FAST-RISING LONG-DURATION OVERPRESSURES

WHEN INCIDENT A N D REFLECTED PRESSURES ARE APPLIED ALMOST SIMULTANEOUSLY*

Animal

species

Mousef

Rabbitf

Guinea pigt

Ratf

DogJ

Overpressure for indicated mortality, psi

1 per cent 50 per cent 99 per cent

Incident

7

9

10

1 0

1 5

Reflected

20

25

28

28

40

Incident

1 1

1 2

1 3

14

17

Reflected

30

33

37

39

48

Incident

15

1 5

1 6

1 8

20

Reflected

44

44

48

53

56

Threshold pressure

for lung injury,

psi

Incident

4

6

6

8

7

Reflected

1 0

1 5

1 5

1 9

20

Man§ 35-45 45-55 55-65 15-25

NOTE: All incident and reflected overpressures were empirically determined. Because of geometric

factors there necessarily was not the same relation between incident and reflected overpressures for ex

periments with the smaller and the larger animals; e.g., the reflection of a given incident pressure is less

in the presence of a larger animal than it is for the smaller animal.

* Reports WT-1467, 3 0 TID-6056, 3 1 TID-5564, 4 4 and unpublished data from an AEC project being con

ducted at Lovelace Foundation, Albuquerque, N. Mex.

tDurations of overpressure were 6 sec.

^Durations of overpressure were 400 msec.

§ Tentative estimate for overpressure durations greater than 50 0 msec.

Table 1 9 XPOSURE TO SLOW-RISING OVERPRESSURES  OF LONG DURATION*

Max.

o v e r p r e s s u r e ,

p s i

1 6 7

1 1 8

156

1708 6

130

Time t o

max.

pressure,

msec

155

8 5

8 6

6 0

2 8

3 0

D u r a t i o n o f

o v e r p r e s s u r e ,

s e c

5

20

20

1 0

1 0

1 0

Ruptured

eardrums

Yes

Yes

Yes

YesYe s

Yes

Damage observ ed

Hemorrhagic

sinuses

Yes

Yes

Yes

YesYes

Yes

Lung

contusion

None

None

Minimal

NoneNone

Minimal

*Richmond et al. 3 2

Table 20 ORBITAL FRACTURE IN DO GS EXPOSED TO SLOW-RISING LONG-DURATION OVERPRESSURES*

Occurrence of orbital fracture for indicated times to maximal pressure (Pm ax )

1 0 to 20 msec 21 to 30 msec Totals 1 0 to 30 msec Totals 31 to 16 0 msjecOver

pressure, Number Orbital % Number Orbital % Number Orbital % Number Orbital %  

psi animals fracture fracture animals fracture fracture animals fracture fracture animals fracture fracture

40-80

81-120

121-160

161-200

201-240

T o t a l s

15

12

9

0

112

4

0

2 0

100

100

44

2

1 0

6

9

1

2 8

0

0

0

3

1

4

0

0

0

3 3

1 0 0

1 4

2

1 1

1 1

1 0

3

3 7

0

0

14

3

8

0

0

9

40

1 0 0

2 2

3

4

6

3

0

1 6

0

0

0

0

0

0

0

0

0

0

0

0

*Overpressure durations ranged from 5 to 20 sec. Data from Richmond, AE C Project, Lovelace Foundation, Albuquerque,

N . Mex. (unpublished)

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Table21MORTALITY DATA FOR GUINEA PIGS EXPOSED AGAINST , AN D AT

VA RIOUS DISTANCES FROM, THE EN D   PLATE CLOSING A SHOCK TUBE TO

FAST-RISING LONG-DURATION OVERPRESSURES W H E N THE INCIDENT AN D

REFLECTED OVERPRESSURES A RE APPLIED IN TWO STEPS*

Distance

from

end plate,

in.

0

1

2

3

6

1 2

Number

animals

1 40

75

78

87

99

1 09

Overpressuref associated

with 50 %   mortality, psi

Incident

12.1

13.4

15.6

16.9

18.7

18.2

Reflected

36.7 .7

40.8 2.1

48.3 1.3

52.8 .9

58.6 1.6

57,1 1.1

Time between applica

tion of incident and re

flected pressures,

msec

Essentially none

0.10

0.20

0.30

0.63

1.36

* Report TID-6056. 3 1

fThe overpressure durations were between 6 and 8 sec.

Table 22 FAST-RISING SHORT-DURATION OVERPRESSURES

REQUIRED FOR NEAR  1 00 PER CENT MORTALITY IN D OGS *

Maximum static

overpressure, psi

Overpressure 

duration, msec

216

219

1 25

85

79

76

1.6

1.6

4.1

8.6

10.3

11.8

*Data from Desaga.

Table 23RELATION BETWEEN OVERPRESSURE A ND 50 PER CENT MORTALITY FOR ANIMALS

EXPOSED TO SINGLE SHARP-RISING OVERPRESSURES OF  INDICATED DURATIONS*

Overpressures for 50 % mortality at indicated durations, psi

Animal

speciesf

Mouse

Rabbit

Guinea pig

Rat

Dog

6 to

Incident

1 1

1 2

13

14

8 sec

Reflected

30

33

37

39

400 msec  (t)t

Incident

1 1

1 2

1 3

1 4

1 7

Reflected

31

33

35

37

48

80 msec (t)J 3 to

Incident Reflected Incident

1 1

1 3

1 4 38 1 3

11

4  msec

Reflected

29

36

35

39

*Data from Report TID-6056 3 1 and unpublished work, AEC Project, Lovelace Foundation, Albuquerque, 

N . Mex.tAnimals exposed against the end plate closing a shock tube to incident and reflected overpressures that

were applied almost instantaneously.

t(t) = tentative data.

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Table 24 PRESSURE TOLERANCE OF THE EARDRUMS OF DO G AND MAN

Maximum pressures for the noted conditions

Species

Dog*

Mant

Minimal,

psi

5

5

Average,

psi

31

20-33

Maximal,

psi

90

43

*Data from 1953, 1955, and 1957 Nevada Field Tests; see WT-1467. 3 0

TData from Zalewski.4 7 Human eardrum tolerance varies with age, hencethe variation from 33 psi (for ages 1 to 1 0 years) to 20 psi (for ages above

20 years). Se e also Report TID-5564.4 4

Table 25 VELOCITY-MASS PROBABILITY RELATIONSHIPS

REQUIRED FOR SM ALL WINDOW-GLASS FRAGMENTS TO

TRAVERSE THE A BD OM I N A L WALL A N D REACH THE

PERITONEAL CAVITY OF DOGS*

Mass of glass

fragments,

g

0.05

0.1

0.5

1.010.0

Impact velocities for indicated

probabilities of penetration in per cent, ft/sec

1 per cent

320

235

1 60

1 40

1 1 5

50 per cent

57 0

41 0

27 5

24 5

1 80

99 per cent

1000

73 0

48 543 0

35 5

*Data from Report AECU-3350. 6

Table 26 EFFECTS OF MISSILES ON H U MAN CADAVERS*

Type

missile

Sphericalbullets

Bullets

Mass,

g

8.7

8.77.4

7.46-106-15

Velocity,

ft/sec

1 9023 0

360

513

420-266

751-476

Effect on man

Slight skin lacerationPenetrating wound

Abrasion and crack of tibia

Travels through thigh

Threshold for bone injury

Fractures large bones

*Data from Journee. 2 7

Table 27 IMPACT VELOCITY REQUIRED FOR PUNCTURING RABBIT

EYEBALL EMBEDD ED IN GELATIN*

Shape

of steelmissile

Sphere

Sphere

Cube

Cube

Cube

Cube

Cube

Mass

Grains

0.85

16.0

2,1

4.2

16.0

64.0

255.0

Grams

0.06

1.04

0.14

0.27

1.04

4.15

16.52

V 5 0 impact

velocity,ft/sec

350

1 5220 5

1 23

11 9

7393

Effect on rabbit eye

Fifty per cent chance

of puncturing wall

of eyeball with loss

of aqueous humor

(fluid).

*Data from Stewart, Report CWLR 2332.

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Table 28 FFECTS OF MISSILE IMPACT O N TH E CHEST AN D HEAD

Threshold velocities for

missiles of indicated weights,  ft/sec

Biological effects observed 0.8 Ib 0.4 Ib

Lung hemorrhages  *

Side of impact only (unilateral)

Impact side and opposite side  (bilateral)

Ri b fracture*Internal lacerations from fractured ribs*

Fatality within 1 hr*

Experimental fracture

human skullf

4511 0

6090

15 5

80

12 5

12 012 0

17 015 to 23 ft/sec range of velocities for

10 Ib object (7-15 Ib weight range ofhuman adult head)

*UnpubIished data from dogs, A EC Project, Lovelace Foundation, Albuquerque, N . Mex.f Computed from data of Gurdjian, Webster, and Lissner. 2 5

Table 29 VELOCITIES OF IMPACT AGAINS T A H ARD SU RFACEASSOCIATED WITH 50 PER CENT MORTALITY OF THE INDIC ATED

SPECIES OF ANIMALS WITH EXTRAPOLATION T O M A N * f

Species

of

animal

Mouse

Rat

Guinea pig

Rabbit

Man

(computed)

Averageanimal

mass,

g

19

18 0

65 0

2,600

72,574

(160 Ib)

Impact velocity for

50 per cent mortality

Ft/sec

38

44

31

31

27

M ph

26

30

21

21

18

Equivalent height of fall

(approx.),

ft

22

30

15

15

11

NOTE: The regression equation fitted to the animal data an d used in

computing the predicted V 5 0 for man is

log V 5 0 = 1.6792-0.517 log m

V 5 Q   = velocity associated with 50 per cent mortality infeet per second and m = average weight of the ani

mal in grams.  Standard error for estimating V 5 0 is

0.0448 log units or about 10.5 per cent.

*National Safety Council release on urban automobile accidents shows

40 and 70 per cent of  fatalities were associated, respectively, with  speeds

of or less than 20 and 30 mph t Quoted from DeHaven. 1 5

tData AEC Project, Lovelace Foundation, Albuquerque, N . M ex ,

Table 30 APPROXIM V E IMPACT VELOCITIES AN D EQUIVALENT HEIGHTS OF DROP

FOR FRACTURE OF H U M A N SPINE, SKULL, FEET, AN D ANKLES

Effects on man

Experimental

skull fracture*

Fracture of feet

and anklesf

Fracture of

lumbar spinet

Impact

Ft/sec

13.5-22.9

12-13

8

velocity

M ph

9.5-15.0

8-9

6

Equivalent

height of drop,

in.

37-91

25-30

12

Comment

Range of 1   to 99 per cent frac

ture of cadaver heads dropped

on flat metal surface

Impact-table data using cadavers

with knees locked

Estimated for impact on hard

surface in sitting position

*Data from Gurdjian,  Webster, and Lissner. 2

fData from Draeger et al. 1 7  

JComputed from data of Ruff. 3 4

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Table 31 HERMAL ENERGIES FOR B URNS OF BARE WHITE SKIN*

Thermal energy for the indicated

explosive yields, cal/cm2

Degree of burn 1 kt 20 kt 10 0 kt 1 M t 10 Mt 20 Mt

First degree

Second degree

Third degree

2.0

4.1

6.0

2.5

4.9

7.3

2.7

5.4

8.1

3.2

6.2

9.4

3.77.2

10.8

3.87.5

11.4

*Data from

Table 32 COMPARISON OF THERMAL ENERGIES

APPLIED OVER 540 MSEC REQUIRED FOR BURNS OF

THE SKIN OF WHITE  AND NEGRO VOLUNTEERS*

Thermal energy, cal/cm2

Degree of burn White subjects Negro subjects

NoneFirst degree

Second degree

Third degree

2.0

3.2

3.9

4,8

Not stated

Not stated

1.8-2.9

3.3-3.7

*Data from Evans et al. 1 9 and Brooks et al. 7

Table 33 MORTALITY IN TREATED BURN CASESRELATED TO PERCENTAGE OF BODY AREA BURNED*t

Average mortality

read from probitcurve, %

1

10

20

30

40

50

60

70

80

90

95

Area burned,

% of totalbody area

22

4149

55

60

65

70

75

81

89

96

* Number of cases, 405.

tData from Schwartz, Soroff, Reiss, and Curtis, Re

port MEDEW-RS-12-56. 3 6

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Table 34 STIMATED RELATIVE IMPORTANCE  OF CONCOMITANT

SECOND- AND THIRD-DEGREE BURNS ASSOCIATED WITH AN

AVERAGE MORTALITY OF  50 PER CENT IN TREATED CASES*t

Third-deg ree

burn a r e a , %

4 6

4 0

3 5

3 0

2 5

Second-degree

burn a r e a , %

0

1 1

2 1

3 0

3 9

T h i r d -degree

burn a r e a , %

2 0

1 5

1 0

5

0

Second-de gree

burn a r e a , %

48

5 7

6 7

7 6

8 5

* Number of cases, 405.

fData from  Schwartz, Soroff, Reiss, and Curtis, Report MEDEW-RS-

12-56. 3 6

Table 35   STIMATED  HEALING  TIME FOR FIRST-,  SECOND-, AND THIRD-DEGREE

BURNS AND SIMPLIFIED  CLINICAL COMMENTS*

Degree ofburn

Healing time,

days Comments

First 8

Second 8-16 (uninfected)

Up to 42 (infected)

Third 2 0 to 30 (uninfected

small burns

epithelize)

2 0 to 42 (larger burns

healing with scar

formation)

Many months (skin

grafting required)

Burning pain 2 4 hr; soreness and redness 8 days

Intense burning pain 2 4 hr; swelling by   1 hr (can

be very serious if face is involved)

Blistering 2   to 30 hr; ooze serum 34 days; scar

(scabbing) 6 to 10  days; aching and tenderness 

8 4 days

Brief intense pain followed by blanching and sub

sequent insensitiveness to pin prick; swelling

up to 2 days (can be very serious if eyes and

lips are involved); blistering around third-

degree burn, 24-36 hrs; soreness  7-10 days

Separation of destroyed skin 3 to 4 weeks with

ulceration; epithelization 4 weeks (small

burns); scar formation 6 weeks; areas wider

than 2 cm (0.8 in.) require plastic surgery

*Data from Butterfield, Seager, Dixey, and Treadwell. 8

Table 36 PROBABLE EFFECTS IN HUMANS OF ACUTE

EXPOSURE TO IONIZING RADIATION OVER THE WHOLE BODY*

Acute dose,

r Probable effect

0 25  No obvious injury

25 50  No serious injury; possible blood changes

50-100 Blood-cell changes; some injury; no  disability

100-200  Injury; possible disability

200 400 Injury and disability certain; death possible

400 Fatal to 50 per cent

600 or more Fatal

*Data from U. S . Department of  

Health, Education and Welfare,2 8 citing

as the source of the information.

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Appreciation of the hazard to man from retinal burns resulting from fireball light isapparently far from complete, particularly for bursts above or in the high terrestrialatmosphere. However, a few data are at hand from experience during Operation Hard

tack in 1958* when two devices in the megaton range were detonated in the vicinity ofJohnston Island, one at an altitude of about 100,000 ft and the other above 200,000 ft. The

latter explosion did not produce an intensity of thermal radiation on the earth's surface

at Johnston Island sufficient to produce first-degree burns in humans* N o data were obtained from the lower explosion because of cloud cover. A biomedical project employing

rabbits to investigate the hazard of burns to the retinal tissue of the ey e observed retinal

burns (0 .5 mm) out to distances of 345 miles. This involved a potential hazardous area

of near 374,000 square miles in clear weather. It was concluded that an individual wouldhave to be looking directly at the fireball of a nuclear detonation to receive permanent,

serious impairment of vision from a high-altitude burst.

IONIZING-RADIATION EFFECTS

The probable early effects in humans of acute exposure to varying doses ofionizing radiation over the whole body are listed in Table 36. 2 8

exposure to radiation is no t acute bu t is prolonged, some tissues of the

body undergo repair, an d the degree of the biological effect depends, among other things,

upon the balance maintained between the continuing repair and radiation damage. For

doses accumulated over a one- or two-day period, the repair process is not very effec

tive, but, on an d after the third day, particularly at low dose rates, very appreciable dif

ferences occur. Tables 37 and 38 summarize applicable estimates made by the U. S.

Public Health Service. 2 8 Long-term genetic effects attributable to exposure to ionizing

radiation above the natural background (4.3 to 5.5 r over 30 years in the United States)

are no t clearly definable. However, responsible individuals have estimated that from 30

to 8 0 r accumulated dose would double the mutations that occur spontaneously. In view

of this, a Genetics Committee of the National Academy of Sciences 5 0 has recommended

that radiation exposure (1 ) be held as low as possible, (2 ) as an average for the popula

tion, be limited to no t more than 10 r accumulated dose to the reproductive organs up to

the age of 30 years, and (3 ) be limited for individuals to 50 r to the reproductive organs

up to age 30 an d to 50 r additional up to the age 40.

It is of interest to note here that a responsible body of scientists hasconsidered the question of the maximal permissible radiation exposure in case of an

emergency. The following statement was made: However, it can be stated with some

confidence that total doses of 150 to 20 0 r, delivered acutely or over days or months,would result in no apparent acute effects and serious late effects in only a small percent

of those exposed, "tSuch an opinion is consistent with experience gained in human radiation acci

dents and treatment summarized by Gerstner. 2 2 ' 2 3 This author also noted the percentage

of the exposed population that might require hospitalization. The data, along with a very

general assessment of the clinical course, are noted in Table 39.

* Joint A E C - D O D News Release, dated June 15, 1959. 5 2

tNational Academy of Sciences National Research Council Report,

p. 17 , 1958 . 5 1

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Table 37 STIMATE OF EFFECTIVE DO SE A N D LETHALITY OF VARIOUS

DOSE RATES TO MAN*t

Dose,

r/day

200

10 0

50

Day

1

3

5

1 0

1

3

5

1 0

1

3

5

10

1 5

Accumulated

dose, r

20 0

600

1000

2000

10 0

300

50 0

1000

50

150

250

50 0

75 0

Effective

accumulated

dose,  r

20 0

542

81 9

1326

100

271

409

66 3

50

13 5

204

33 0

395

Estimated mean

survival time,

days

20

1 5

1 0

1 5

1 5

30

30

30

Estimated per

centage of deaths

in 30 days

30

60

85

100

8

35

50

75

0

1 5

25

40

50

*From

tBased on 250-kvp X rays.  Corrections should be made for higher energy radiations; e.g.,

1000-kvp X or gamma radiation would have a relative biological effectiveness of approxi

mately 70 per cent of 250-kvp X rays.

Table 38 ESTIMATED DOSES  FOR VARYING DEGREES OF INJURY TO MAN*?

Dose rate,

r/day

50 0

10 0

60

30

1 0

3

0.5

Period of

time

2 days

Until death

1 0 days

1 0 days

36 5 days

Fe w months

Many months

Effect

Mortality close to 10 0 per cent

Mean survival time approximately 1 5 days

1 00 per cent mortality in 30 days

Morbidity and mortality high with

crippling disabilities

Disability moderate

Some deaths

N o drop in efficiency

N o large-scale drop in life span

*From

tBased on 250-kvp X rays. Corrections should be made for higher energy radi

ations; e.g., 1000-kvp X or gamma radiation would have a relative biological effec

tiveness of approximately 70 per cent of 250-kvp X rays.

Table 39 ESTIMATED CLINICAL COURSE A N D HOSPITILIZATION REQUIREMENTS FOR

HU M ANS EXPOSED TO VARIOUS ACUTE DOSES OF PENETRATING RADIATION*

Individuals following indicated Individuals

T^M clinical symptoms, % _ nA.,. in?.Dose, hospitilization,

r Trivial Light Moderate Serious Grave Fatal

0-200 98 2

200-300 1 33 64 2

300-400 6 68 26

400-500 3 58 39

500-600 6 94

Above 600 10 0

%

None

2

941 00

10 0

10 0

Maximal

time of

hospitilization,weeks

0

6

7

9

1 1

1 1

"Compiled from Gerstner,2 2 ' 2 3

45

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Q U ANTITA TIVE W EAPONS-EFFECTS D ATA

T he material that follows, along with the explanatory remarks for each table or illustration, sets forth selected weapons-effects data, all referable to sea-level surface altitudes, as a

function of explosive yield for surface and typical air bursts. S om e assessment of the com

parative hazard to man from blast, thermal radiation, and ionizing radiation can be obtained by  referring to previous sections of the brochure.

Perhaps the reader will  share with the authors the conclusion that planned protection from

weapon-produced variations in   the environment is desirable and that provision of such protec 

tion would markedly enhance the chances of survival for a high percentage of the population

should nuclear war ever occur.

47

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Comparison of Blast, Thermal Radiation, and Ionizing Radiation

TABLE 4 0 : WEAPONS-EFFECTS DATA FOR SELECTED PARAMETERS

In Table 40 are tabulated the approximate ranges from Ground Zero (GZ) and the circularareas over which the indicated selected weapons effects may occur as a function of explosive

yield. It was assumed that slant ranges for initial ionizing radiation and thermal data are a

reasonable approximation of the ground range an d that atmospheric conditions were clear.

(Data are from

Explosive yield

Selected parameters Ikt 20 kt 100 kt 1 Mt 10 Mt 20 Mt

700 rem (initial)

100 rem (initial)

3 0 rem (initial)

5 psi (typical air burst)

5 psi (surface burst)

1 psi (typical air burst)

1 psi (surface burst)

Second~degree burns

First-degree burns

Fireball

Crater (surface burst, dry soil)

700 rem (initial)

100 rem (initial)

30 rem (initial)

5 psi (typical air burst)

5 psi (surface burst)

1 psi (typical air burst)

1 psi (surface burst)

Second-degree burns

First-degree burns

Fireball

Crater (surface burst, dry soil)

0.42

0.62

0.74

0.39

0.28

1,00

0.86

0.48

0.69

0.044

0.012

Range from GZ for Various Parameters, Miles

0.70

0.99

1.18

1.06

0.77

2.71

2.35

1.72

2.47

0.14

0,031

0,96

1.29

1,51

1.81

1.32

4.64

4.02

3.40

4.97

0.28

0.058

1.44

1.81

2.07

3.90

2.85

10.0

8.65

9.00

13.3

0.69

0.12

2.04

2.55

2.91

8.40

6.14

21.5

18.6

23.8

36.0

1.7

0.26

2.27

2.88

3.30

10.6

7.74

27.1

23.5

31.9

49.2

2.3

0.32

Area Corresponding to Above Ranges, Square Miles

0.55

1 . 2 1

1.72

0 . 4 8

0.25

3.14

2.32

0.73

1.50

0.006

0 . 0 0 0 4 5

1 , 5 4

3 . 0 8

4 . 3 7

3 . 5 3

1 . 8 6

23.1

1 7 . 4

9 . 2 9

1 9 . 2

0.062

0.0012

2.90

5 . 2 3

7 . 1 6

1 0 . 3

5 . 4 7

6 7 . 6

5 0 . 8

3 6 . 3

77.6

0 . 2 5

0.0096

6 . 5 1

10.3

1 3 . 5

47.8

25.5

3 1 4

2 3 5

2 5 4

5 5 6

1 . 5 0

0.045

1 3 . 1

20.4

26.6

2 2 2

1 1 9

1 4 5 0

1 0 90

1 7 8 0

4 0 7 0

9,08

0 . 2 1

1 6 . 2

2 6 . 1

3 4 . 2

3 5 3

1 8 9

2 3 1 0

1 7 3 0

3 2 0 0

7 6 0 0

16.6

0.32

48

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TABLE 41: COMPARATIVE WEAPONS-EFFECTS DATA

Table  41 gives the approximate ground ranges in miles for selected values of initial  ioniz

ing radiation,  overpressure, and thermal radiation computed for typical air bursts of indicated

yields assembled in such a way as to aid appreciation of the interrelation between the individ

ual effects. For example, a ground range of about 3 miles is  shown for 100-rem initial radia

tion from a 20-Mt detonation; at this distance an overpressure near 19 psi can be expected

along with a thermal load of over 1000 cal/cm2 . Ten miles from GZ, 1 psi is predicted for a

1-Mt explosion; at this location there would occur less than 10 rem and about  6 cal/cm2 of

initial ionizing and thermal radiation, respectively. Referring to Table 31, one can see that

6  cal/cm 2 of thermal energy is sufficient to produce second-degree burns to the exposed bare

skin.

Since the data in Table 41 are for typical air bursts, no significant short-term fallout

hazard would occur. As in the previous table, slant ranges for ionizing and thermal radiations

were considered to be a reasonable approximation of the ground  range.

The symbols > and »mean greater than and much greater than, < and «mean less  than 

and much less than,  respectively.

(Data are from 

Initial ionizing radiation,

overpressure, and thermal

radiation Ikt 20 kt 100 kt 1 Mt 10 Mt 20 Mt

30-rem range,  miles

Pressure, psi

Thermal, cal/cm2100-rem range, miles

Pressure, psi 

Thermal, cal/cm27 00- rem range,  miles

Pressure, psi

Thermal, cal/cm21-psi range, miles

Radiation, rem

Thermal, cal/cm25-psi range, miles

Radiation,  rem

Thermal, cal/cm2Second-degree burn:

Range, miles

Pressure, psi

Radiation, rem

0.74

1.70

1.70.

0.62

2.30

2.50

0.42

4.3

6.9

1.00

0.88

0.39

900

7.00

0.48

3.6

380

1.18

4.16

12.4

0.99

5.55

18.0

0.70

9.1

38

2.71

2.02

1.06

64

15,8

1.72

2.2

<1 0

1.51

6.60

36.0

1.29

8.30

52.0

0,96

11.2

97

4,64

3.30

1.81

< io

24.5

3.40

1.7

<10

2.07

11.1

18 2

1.81

12.4

240

1.44

14.9 

400

10.0

5.90

3.90

<10

46.0

9.00

1,2

<10

2,91

15,6

880

2.55

17.4

>1000

2.04

20.5

X L O O O

21.5

11,4

8.40

<10

89.0

23.8

<1

«10

3.30

17.0

>1000

2.88

18.8

>1000

2.27

22.5

>1000

27.1

13.8

10.6

<1 0

105

31.9

< 1

«10

49

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FIGURE 3: ENVIRONMENTAL VARIATIONS DU E  TO BLAST, THERMAL RADIATION ,  AN D

IONIZING RADIATION FOR INDICATED EXPLOSIVE YIELDS

The scaled ranges and areas applicable to 10 0 rem of initial radiation, 1 psi, and second-

degree burns for typical air bursts are shown in Fig. 3   as these parameters vary with explo 

sive yield. The relative gain in  range and areas covered by blast and thermal effects compared 

with initial ionizing radiation as weapon weight increases deserves  emphasis. For yields of  1

M t or less, the areas in which at least second-degree burns will occur are smaller than those

for at least 1-psi overpressure; whereas for the higher yields the reverse is true. Slant ranges

for ionizing and thermal radiation were assumed to be reasonable approximations of the ground

range. (Data are from

IKT 20 KT 100 KT 10 MT 20 MT1-40

- 0

-20

SecondDegree —b— —

Burn* f

Second Degree Burns

Second Degree Burns

-10

-20

<-40

50

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FIGURE 4: ENVIRONMENTAL VARIATIONS DUE TO BLAST, THERMAL RADIATION, A N D

INITIAL IONIZING RADIATION FOR 1-, 20-, 100-, A N D 1000-KT EXPLOSIVE YIELDS

The scaling relations for 30 and 10 0 rem of initial radiation, 1 and 5 psi, and second-

degree burns are shown to the same scale in Fig. 4 for typical air bursts ranging from 1 kt to

1 M t. The reader will note that the 100-rem radius extends well beyond the 5-psi line for a

1-kt yield. These tw o radii are almost equal for 20 kt, bu t the 5-psi line extends much beyondthe 100~rem range for yields of 100 and 1000 kt. Slant range for ionizing and thermal radiation

was considered a fair approximation of the ground range. (Data are from

20 KT 100 KT I MT

IO O RE M (2.3 PSI)Range: 0.62 m iAr ea: 1 . 2 1 tq mt

30 REM (1.70 PSI)Range: 0.74 m iArea: 1.72 sq ml

5 PSIRange: 0.390 m iArea: O.478 s q mi

IO

100 REM (8.3 PSI)Range: 1 .29miAr ea: 5.23 s q m t

30 REM (6.6 PSI)Rang*: 1 . 5 1 miArea: 7.16 s q m l

Second Degree BuRange: 0.485 m iArea: 0.739 s q m i

Second Degree BurnsRange 1.72 m iAreo 929 m i

I Range: 1 . 8 1 ml

Range 4 64mi Area: 10.3 sq m iArea: 67.6 s q m i

Second Degree BurnsRange. 3.40 miArea: 36.3 sq m i

100 REM (J2.4 PSI)Ra nge : 1 . 8 1 m iArea: 10.3 s q m i

30 REM ( 1 1 . 1 PSI)R ang*: 2.07 m lArea:13.5 s q m i

r 0

-

-

-0

PSIR ange: 3.9OmiArea: 47.8 s q m i

51

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FIGURE 5: ENVIRONMENTAL VARIATIONS D UE TO BLAST, THERMAL RADIATION, AN D 

INITIAL IO NIZING RADIATION   FOR  1- AN D 10-MT EXPLOSIVE YIELDS

A comparison of the  radii and ranges for 1 - and 5-psi blast overpressure,  30 and 10 0 rem

of initial radiation, and second-degree burns is shown to the same scale for typical air bursts

of 1- and 10-Mt yields. Slant ranges for ionizing and thermal radiation was  assumed to be a

reasonable approximation of the ground range. (Data are from

\   MT

Total initial Dose

of 100 REM(12.4 PSI)

' Ra nge: 1 . 6 1 miArea: 10.3 sq m i

Total Initial Dose

of 100 REM (174 PSI)

Range: 2.55 mi

Area   : 20.4 sq m i

10 MT

5 PSf

Range: 3.90 mi

Area: 47.B sq mi

10 --Second Degree Burns (1.2 PSI) 

Range: 9.00 m i

Area: 254 sq m i

60 sq mi

I PS IRange. 1O.O mi

Area: 31 4 s qm i

320sq m i

-25

-20

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FIGURE 6 : ENVIRONMENTAL VARIATIONS DUE TO  BLAST, THERMAL RADIATION, A N D

INITIAL IONIZING RADIATION FOR A   20-MT EXPLOSIVE YIELD

A comparison of the indicated effect parameters is shown for the 20-Mt typical air burst

drawn to the same scale as in Fig. 5 . It was assumed that the slant ranges for thermal and

ionizing radiation were reasonable approximations of the ground ranges.

It is instructive to contemplate Fig. 6 from the point of view of human hazard. Exposureto 10 0 rem of initial radiation would cause no incapacitation. However, casualties from ther

mal and blast would  be very high at the 100-rem location, about 3   miles from GZ, where the

overpressure and thermal flux would be close to 19 psi and over 1000 cal/cm 2 , respectively.

Indeed, casualties from blast, flash burns, an d fire would be heavy out to the 5-psi location,

where houses would.be completely destroyed by blast (see Table 2). Still further out, injuries

would lessen and be minimal owing to blast at the 1-psi line where wooden-frame houses suffer

5 0 per cent damage. Serious  flash and fire hazards for unprotected persons would exist o ut to,

and even beyond, the second-degree burn line. One reason for this is the fact that thermal

fluxes required to ignite fine kindling fuels are very close to those which produce second-

degree burns of the bare skin. There would be no immediate fallout problem since the case

under discussion involves an air burst.

(Data are from

Total Initial Dose of

100 REM (18.8 PSI)

Range: 2,88 mi

Area: 26.1 sq mi

30 REM (17.0 PSI)

-5

-0

-25

-20

-15

- 0

-10

-15

-20

- 0

53

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FIGURE 7: ENVIRONMENTAL VARIATIONS D U E TO BLAST, THERMAL RADIATION, A N D

INITIAL IONIZING RADIATION FOR A 1-KT EXPLOSIVE YIELD

Figure 7 shows an expanded plot of selected effects data for a typical air burst at a yield

of 1 kt. It was assumed that slant ranges for ionizing and thermal radiation are reasonable approximations of the ground ranges. (Data are from

-1.0

-.9

-.8

-.6

-.5

- .4

-.3

-.2

-0

-.3

-.4

-.5

-.7

- .8

*— 1,0

54

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FIGURE 8 : ENVIRONMENTAL VARIATIONS DUE TO BLAST, THERMAL RADIATION, A N D

INITIAL IONIZING RADIATION FOR A 20 -KT EXPLOSIVE YIELD

Figure 8 shows an expanded plot of selected effects data for a typical air bursts at a yield

of 20 kt. It was assumed that slant ranges for ionizing and thermal radiation are reasonable

approximations of the ground ranges. (Data are from

100 RE M (5.6 PSI)3.08 sq mi

5 PSI, 3.53 sq mi

30 R E M(4.2 PSI)

I- 2.5

- .0

- .5

-1.0

-5

— 0

-5

— 1.0

— 1.5

 .0

L- 2.5

55

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FIGURE 9: ENVIRONMENTAL VARIATIONS DUE TO BLAST, THERMAL RADIATION, A N DINITIAL IONIZING RADIATION FOR A   100-KT EXPLOSIVE YIELD

Figure 9 shows an expanded plot of selected effects data for a typical air burst at a yield

of 10 0 kt. It was assumed that slant ranges for ionizing and thermal radiation are reasonable

approximations of the ground ranges. (Data are from 2 4 )

100 RE M (8.3 PSI)

5,23 sq mi

30 REM (6.6

7.16 sq m i

PS!)

5 PS I

10.3 sq

— 4

-i 2

L_ rt  0

-

— 3

-

5 6

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FIGURE 10: APPROXIMATE DISTANCE V S. YIELD RELATIONSHIPS  FOR OVERPRESSURE,

THERMAL RADIATION, AND  INITIAL IONIZING RADIATION FOR A TYPICAL AIR BURST

Figure 10 summarizes graphically the yield-distance relationships for effects produced by

typical air bursts and allows a comparison of the ground ranges for 30 an d 100 rem of initial

radiation, 1 and 5 psi, an d first- and second-degree burns. It was assumed that clear weather

conditions prevailed and that slant range for ionizing and thermal radiation represented a rea

sonable approximation of the ground range. (Data are from

APPROXIMATE DISTANCE-IELD  RELATIONSHIPS

FOR OVERPRESSURE, THERMAL AN D PROMPT

IONIZING RADIATION FOR THE TYPICAL AIR BURST

I I 1 I I I II I I I I I I I I I 1 I I II III I I I I IIKT 10 KT 100 KT IMT

EXPLOSIVE YIELD

10MT

57

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TABLE 4 2 : COMPARATIVE EFFECTS DATA FO R A 20-MT SURFACE BURST (10 MT FIS

SION YIELD)

Table 4 2 presents approximate comparative effects data in tabular form for a surface 

burst of 20-Mt total yield. These data are presented graphically in Fig. 11. The presence of

fallout radiation is the principle  difference between this type explosion and one detonated in the

air. Ranges for the 1- and 5-psi lines are somewhat shorter for the surface burst compared

with the air burst.

Assumptions made in computing the fallout pattern were  (1 ) an effective wind of 15 mph 

and (2 ) 5 0 per cent of the total yield was derived from fission. The latter assumption was

necessary since the fusion process does not contribute significantly to the radioactivity of the

fallout; i.e., the total yield determines the spatial extent of the fallout; whereas the fission 

yield fixes the amount and hence the level of radioactive contamination.

The somewhat hypothetical "1-hr reference dose rates" in roentgens per hour were used

as a means of illustrating the relation between the fallout hazard within the immediate target

area and the blast, radiation, and thermal effects. The 1-hr reference dose rate is defined as

the dose rate 1 hr after the detonation, assuming that fallout were complete at that time. Thesomewhat artificial significance o f these dose rates in terms of accumulated dose is discussed

in connection with Table 4 3 .

(Data are from

Range, miles Area, square miles

A t least first-degree burns 49.2

A t least second-degree burns 31.9

A t least third-degree burns 29.0

At least 1 psi 23.5

A t least 5 psi 7.74

A t least 3 0 rem (initial) 3.30

A t least 10 0 rem (initial) 2.88

At least 30 r/hr fallout (1-hr reference dose rate)

A t least 10 0 r/hr fallout (1-hr reference dose rate)

A t least 3 0 0 r/hr fallout (1-hr reference dose rate)

A t least 1 0 0 0 r/hr fallout (1-hr reference dose rate)

A t least 3 0 0 0 r/hr fallout (1-hr reference dose rate)

A t least 1 psi and less than 30 r/hr

A t least 1 psi and less than 10 0 r/hr

A t least second-degree burns and less than 1 psi

A t least second-degree burns and less than 3 0 r/hr

At least second-degree burns and less than 10 0 r/hr

7 6 0 0

3 2 002 6 4 0

1 7 3 018 9

34.2

26.1

1660*

1240*

895*

489*

183*

881

1240

1460

2110

2800

* Measured only to first-degree burn line. Effective wind assumed to be 15 mph.

5 8

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FIGURE 11 :  COMPARATIVE EFFECTS FOR A 20-MT SURFACE BURST

Figure 11 graphically presents the effects data set forth in   Table 42 referable to a  surface detonation of a nuclear weapon having an assumed fission yield of   1 0 Mt bu t a total yield of20  Mt.

The  somewhat hypothetical fallout contours  in terms of the 1-hr reference dose rates  aredepicted on ly to the first-degree burn limit approximately 49 miles from GZ, although thefallout might actually extend  several hundred miles from the target area as dictated by thewinds aloft. In the illustration a 1 5 mph   effective wind was assumed.

25  20

\

-50

-35

-30

-25

-20

-15

-10

— 0

-10

-15

-20

-25

25  20 15 20 25

5 9

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FIGURE 12 : INFINITY ISODOS E CO N T O UR S FOR A 20-MT SURFACE BURST COMPUTED

FROM WIN D DATA ON FOUR SELECTED DAYS

Infinity isodose contours for penetrating fallout radiation were computed for a 20-Mt sur

face burst (10 Mt fission yield) at Albuquerque for wind patterns of four selected dates. No

radiation shielding was assumed. The computed center of the path of 100-jj, fallout particles isshown to illustrate that winds aloft may change in velocity and direction as a function of time

and hence influence the ground path of particulates falling from various altitudes. Ranges from

GZ and the outline of neighboring states an d cities are also presented to facilitate appreciation

of the shape of areas that may be contaminated with radioactive debris. For areas included in

side the isodose contours, see Table 45. Computations and data were furnished by Sandia Cor

poration, Albuquerque, N . Hex. See C owan 1 3 an d Young  and Bledsoe4 5 for details of the fallout

model employed; see Young 4 6   for a variety of fallout contours similar to those which follow.

Weighted Hociograph for 100 mcron Particle

_ _.__

Lo,Veg«i / / TT J50!?'l-* ^

/ CALIFORNIA

\

Bakenfield

August 1,   1955

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FIGURE 13 : ISODOSE-RATE C O N T O U R S AT INDICATED TIME FOR A 20-MT SURFACE

B U R S T PREDICTED FOR THE WI N D PATTERN OF MA Y 12, 1 9 5 6

Isodose-rate contours for penetrating fallout radiation without shielding were computed for

a 20-Mt surface burst (10 M t fission yield) at Albuquerque for the wind pattern of May 12, 1 9 5 6 ,

showing 100-, 1000-, and 10,000-r/hr contours at 15   min after the explosion and the 100- and

1000-r/hr contours 2 hr after the explosion. H-hour indicates zero time or the moment of the

burst. H + V   and H + 2 hr denotes time  V4 and 2 hr after the detonation, respectively. For

areas inside the contours, see Table 4 4 . Computations and data were supplied by  Sandia Cor

poration, Albuquerque, N. Mex.

14 0

120-

100

80

70

60

30

20

20-

30 L

Roton.

Questa* • Red River

• Cuba

Springer

.Wagon Mound

1,OOOr/V(H + 2)

100 r/Kr (H + 1/4)

1,000 r/hr (H +1/4)

10,000 r/hr (H + 1/4)

12 0 130

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FIGURE 14: I SOD OSE C O N T O U R S FOR A 20-MT SURFACE B U R S T PREDICTED FOR THE

WIND PATTERN OF MAY 12 , 1956

Isodose contours were computed for penetrating fallout radiation without protection orshielding for a 20-Mt surface burst (1 0 Mt fission yield) at Albuquerque for the wind pattern

of M ay 12, 1956 , showing the regions inside which the accumulated exposure dose would be

100 , 400, 1000, 4000, r or more at H + 1 and H + 2 hr; i.e., 1 and 2 hr after the detonation.

Note the "embryonic" hot spot enclosed by the 4000-r isodose contours. See Table 45 for

areas enclosed within the several labelled portions of the chart. Computations and data were

supplied by Sandia Corporation, Albuquerque, N . Mex.

90-• E l Ri to

80 -

70 -

60-

• C u b a

50

40

30

20

10

0

10

20

30

-

-

-

-

-

*Correo

• Sa n Felipe Puebl o • Cerrillos

• Madrid

• Ed g e wood

'? „——-, 100r{H+1) ~~*-" ~ ~ —————•——— >

• Lo s Vegas

Clines C or ne r s

i Tajique E t t a n c t a

Vaughn

40 30 20 20 30

Miles

40 60 70 80 90

63

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FIGURE 15: INFINITY  ISODOSE CO N T O UR S FOR A 20-MT SURFACE BURST PREDICTED 

FOR THE WIND PATTERN OF MAY 12 , 1956

Infinity isodose contours for penetrating fallout radiation at "near" ranges for a 20-Mt

surface burst (1 0 Mt  fission yield) at Albuquerque were computed using the wind pattern ofMay 12 ,  1956, and assuming no shielding or countermeasures to minimize radiation exposure.

Note the 8000-r hot spot near the northeast corner of the city. Computations and data were

supplied by Sandia Corporation, Albuquerque, N. Mex.

90

80

70

60

50-

40

30

20

10

20

3030 ~

Cuba

Cl ines Corne rs

L o s Lunas .

Bel en

* Eftancio

20 10 20 30 40 50

Miles

60 70 80 90 100 1 10

64

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FIGURE 16: ISODOSE-RATE C O N T O U R S AT INDICATED TIMES FOR A 20-MT SURFACE

B U R S T PREDICTED FOR THE WIND PATTERN OF AU G. 1, 1956

Isodose-rate contours for penetrating fallout radiation (unshielded) were computed for a 20-

M t surface burst (10 Mt fission yield) at Albuquerque for the wind pattern of Aug. 1, 1956 ,showing the 100-, 1000-, and 20,000-r/hr contours for H + V   hr, and the 100- and 1000-r/hr

contours at H + 2 hr. Note the difference in shape of the Vi-hr compared with the 2-hr contours

and the similarity to the isodose contours in Fig. 17, where remarks relevant to the wind pat

tern are set forth. Computations and data were supplied by Sandia Corporation, Albuquerque,

N . Mex.

• L o s A lam os

50

40

30

10

10-

20-

30 -

Correo 10 0 r/W (H + 1/4) \\,

l,000r/hr

11 1 eta

Santa Fe

> P«cos

• Clmei Corners

E s t anc ia

40 30 20 20 30

65

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FIGURE 17: IS O DO S E C O N T O U R S FOR A 20-MT SURFACE B U R S T PREDICTED FOR THE

WIND PATTERN OF AU G. 1, 1956

Isodose contours were computed for penetrating fallout radiation without shielding for a

20-Mt surface burst (10 Mt fission yield) at Albuquerque for the wind pattern of Aug. 1, 1956,showing the regions inside which the accumulated exposure dose would have been 100, 400 ,

1000 , and 5000 r or more at H + 1 and H + 2 hr. Note the drift of the higher dose contours toward the north and slightly east; whereas the lower dose contours are more symmetrical and

are generally centered to the northwest. Such behavior of fallout reflects the fact that the

lower altitude winds are blowing toward the north and east, and those at higher altitudes aremoving to the northwest, facts which are reflected by the computed ground path of the 100-jj,

particle shown in the hodograph for Aug. 1, 1956, in Fig. 12. Computations and data were sup

plied by Sandia Corporation, Albuquerque, N . Mex.

70

60

50

40

20

.Chaco Canyon

.Grants

.Cuba.Eiponola

. Los Alamos

100r{H

.Santa Fe

Las Vega*.

.Moriarty

Eitancla

•C lines Camera

Vaughn.

.Bemardo

.Mountafnair

. Scholle,,,..-— —

J O — — — — 70 60 50 40 30 20 10 0 10 20 30 40 X> 6U >U bUMiles

66

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TABLE 44: AREAS (IN SQUARE MILES) ENCLOSED WITHIN SPECIFIED ISODOSE-RATE

CONTOURS  COMPUTED FOR PENETRATING FALLOUT RADIATION AND UNSHIELDED

CONDITIONS FROM A 20-MT SURFACE BURST (10 MT FISSION YIELD) AT ALBUQUERQUE 

USING WIND PATTERNS OF INDICATED DATES

Computed and assembled from data supplied by Sandia Corporation, Albuquerque, N. Mex.

Areas for specified isodose-rate contours, square miles

b u r s t winds

15 min 8-1-555-12-56

8-1-56

5-12-54

2 hr 8-1-555-12-56

8-1-56

5-12-54

1 0 0 r/hr

400

640

390

9000

6300

200 r/hr

390

610

370

7800

51 00

400 r/hr

370

600

360

6300

4100

700 r/hr 1 000 r/hr 4000 r/hr

360

5 8 0

340

6400

4000

3400

35 0

570

330

Not computed

3 0 0 0

2800

3 1 0 0

Not computed

3 1 0

3 7 0

2 8 0

3 2 0

5 8 0

3 6 0

1 0 , 0 0 0 r/hr

2 9 0

2 8 0

260

110

20 0

23 0

20 ,000 r/hr

270

230

170

90

150

TABLE 45: AREAS (IN SQUARE MILES) INCLUDED WITHIN SPECIFIED ISODOSE CONTOURS

COMPUTED FOR PENETRATING FALLOUT RADIATION AND UNSHIELDED CONDITIONS

FROM A 20-MT SURFACE BURST (10 MT FISSION YIELD) AT ALBUQUERQUE USING WIND

PATTERNS OF INDICATED DATES

Computed and assembled from data supplied by Sandia Corporation, Albuquerque, N. Mex.

Time  Date

after of

burst  winds

1 hr 8-1-555-12-56

8-1-56

5-12-54

2 hr 8-1-555-12-56

8-1-56

5-12-54

Infinite 8-1-555-12-56

8-1-56

5-12-54

Areas for specified isodose contours, square miles

100 r

3,300

2,900

3,400

4,800

5,800

4,600

36,000

52,000

44,000

39,000

200 r

1,200

1,100

730

3,400

1,500

4,100

28,000

36,000

26,000

24,000

400 r

450

510

410

2,400

600

2,500

21,000

22,000

16,000

16,000

700 r 1000 r

390 350

360 330

380 320

Not computed

880 470

430 410

730 420

Not computed

15,000 12,000

13,000 9,500

12,000 8,900

12,000 9,200

4000 r

250

300

240

290

330

260

1,500

580

3,500

2,700

10,000 r

200

170

220

210

170

230

330

230

355

450

20,000 r

66

12 0

160

170

i on

67

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TABLE 46: COMPUTED AREAS FOR PENETRATING FALLOUT RADIATION INSIDE INDI

CATED ISODOSE CONTOURS AT SPECIFIED TIMES AFTER DETONATION FOR VARIOUS

EXPLOSIVE YIELDS

A 15-mph wind was assumed at all altitudes and 100 and 50 per cent fission yields were

assumed for kiloton and megaton yields, respectively. (Data are from

2 4 )

Time

after

burst

1 hr

2 hr

24 hr

1 week

1 month

Infinite

Total

explosive

yield

Ikt

20 kt

100 kt

1 Mt

10 Mt

20 Mt

Ikt

20 kt

100 kt

1 Mt

10 Mt

20 Mt

Ikt

20 kt

100 kt

1 Mt

10 Mt

20 Mt

Ikt20 kt

100 kt

1 Mt

10 Mt

20 Mt

1 kt

20 kt

100 kt

1 Mt

10 Mt

20 Mt

1 kt

20 kt100 kt

1 Mt

10 Mt

20 Mt

Areas

100 r

2.0

19

62

3 40

1,300

1,900

2.7

29

98

600

2,400

3,500

5.6

74

3 10

2,300

12,000

16,000

7.1110

460

3,700

23,000

32,000

7.8

120

520

4,400

29,000

44,000

8.4

13 0560

4,700

32,000

56,000

for specified isodose

3 00 r

0.72

9.3

34

23 0

1,000

1,500

1.0

13

52

370

1 ( 700

2,400

2.2

32

150

1,100

6,200

9,400

2.844

220

1,600

11,000

16,000

3.0

48

240

1,900

13,000

21,000

3.2

52260

2,000

14,000

25,000

contours,

1000 r

0.20

3.6

16

150

800

1,200

0.28

5.0

23

210

1,200

1,700

0.63

11

52

500

3,200

4,900

0.8215

72

700

5,000

8,000

0.88

16

8 0

800

5,900

10,000

0.93

188 7

840

6,500

12,000

square miles

3000 r

0.041

1.1

6.6

8 2

58 0

920

0.063

1.6

9.2

110

760

1,200

0.16

3.6

20

210

1,500

2,600

0.224.8

26

270

2,100

3,800

0.25

5.4

28

3 00

2,400

4,400

0.26

5.730

3 20

2,700

5,200

68

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FIGURE 18: DIRECTION OF FALLOUT FROM A 20-MT SURFACE BURST AT ALBUQUER

QUE FOR  SUMMER SEASONS COMPUTED USING W IN D DATA SAMPLED RANDOMLY (BI

MONTHLY OVER FIVE YEARS)

The computed ground pathways (weighted hodographs) of 100-ju . fallout particles from a20-Mt surface burst (10 Mt fission yield) at Albuquerque are presented. Such hodographs gen

erally indicate the center of the fallout path. Although this is not always precisely true, the

accuracy is sufficient to illustrate the variable nature of the winds during the summer season.

Note that the lower altitude winds  may move radioactive debris away from the city in one di 

rection only to have those at higher altitudes sweep the fallout back over or near the point of

burst. On the average, particles from the lower altitudes fall at the nearer ranges and those

from the higher regions fall at the farther ranges from GZ. Data and computations were sup

plied by Sandia Corporation,  Albuquerque, N. Mex.

69

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FIGURE 19 : DIRECTION OF FALLOUT FROM A 20-MT SURFACE BURST AT ALBUQUER

QUE COMPUTED USING W I N D DATA SAMPLED RANDOMLY (BIMONTHLY OVER FIVE

YEARS)

The ground paths of 100-ja fallout particles were computed for a 20-Mt surface burst (1 0

M t fission yield) at Albuquerque. Assuming the hodographs indicate the general direction of the

fallout, it is clear that though the prevailing winds in the Albuquerque area are toward the

east, there is no sector in and about the city and state which might not be contaminated; e.g.,

the winds aloft on any given da y would control the fallout pattern, and from da y to day are so

variable as to make it imprudent to assume any sector of the state would escape fallout. Too,

there is the problem of fallout from cities on the west coast and nearby states to consider.

Over-all the only sound conclusion useful in planning is that all portions of the city and nearby

environs are potential recipients of fallout. The corollary of this is that fallout protection is

indicated for all sectors about the target area an d that this is so even if warning of an immi

nent attack were followed by preburst evacuation. S ee subsequent figures for probability data.

Data and computations were supplied by Sandia Corporation, Albuquerque, N . Mex.

—E

70

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FIG URE 20: PROBABILITIES FOR FALLOU T  GAM M A  RADIATI ON FROM   1-MT BURST 

(S UM M ER  SE ASO N)

The probability contours inside which the infinity exposure dose from penetrating fallout

radiation wou ld be  100 r or more (unshielded) were computed for a 1-Mt surface burst (%   fis 

sion yield) at Albuquerque using wind data over five years for the  summer seasons are pre 

sented. Compare with Fig. 21 for the winter season, and note that almost all the area of the 

city lies well  inside the 0.5 probability line.  Data and computations were supplied by Sandia

Corporation, Albuquerque, N. M ex.

Sp r i n ger

Wagon MoundRoy

Tucumca ri

Magdaleno • Soco rr o

71

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FIGURE 21: PROBABILITIES FOR FALLOUT GAMMA RADIATION FROM 1-MT BURST

(WINTER SEASON)

The probability contours inside which the infinity exposure dose from penetrating falloutradiation wou ld be 100 r or more (unshielded) were computed for a 1-Mt surface burst ( 2/   fis

sion yield) at Albuquerque using wind data over five years for the winter seasons. Compare

with Fig.  20 for the summer season, and note the difference in direction of the long axis of the 

several probability contours. Computations and data were supplied by Sandia Corporation,

Albuquerque, N . M ex .

r80

-60

-40

-2 0

CubaWf l 90n Mound .

L o s A l a m o s• Ro y

? 1 » Sa n ta Fe

_ Sa n Yi i d ro• L a s Vegai

T u c u m c ar i

-20

-40B e rn a rdo

C l ov i s ,

Po r ta l w

-60,MagdaIena

So c o r ro•Elida

L B O40

L 20 20 40I i I

60 80 1 00 1 2 0 14 0I i I i I

16 0I i

18 0_J

Corrizozo.

Miles

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FIGURE PROBABILITIES FOR FALLOUT GAMMA RADIATION FROM 20-MT BURST

(SUMMER S EAS ON)

The probability contours inside which the infinity exposure dose from penetrating fallout

radiation would be 1 00   r or more (unshielded) were computed for a 20-Mt surface burst (1 0  M t

fission yield) at Albuquerque using wind data over five years for the summer seasons. Com

pare with Fig. 20 showing similar summer-season data for a 1-Mt yield, and note the shift of

the long axis of the probability contours from northeast to northwest. This is so because thecloud and stem heights for the 20-Mt yield are higher than those for the 1-Mt burst and there

fore fission debris is subject to transport by the winds at the higher altitudes, which, for the

summer season, generally blow more to the northwest and west. Data and computations were

supplied by Sandia Corporation, Albuquerque, N. Mex .

"H O

Ch om o

Ra ton

Cimar ron

Spr inger

40 60 80 100 12 0

1 . I . I * IMiles

73

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FIGURE 23: PROBABILITIES FOR FALLOUT GAMMA RADIATION  FROM 20-MT BURST

(WINTER SEASON)

The probability contours  inside which the infinity exposure dose from penetrating fallout radiation would be  100 r or more  (unshielded) were computed for a 20-Mt  surface burst  (1 0 Mt fission yield) at Albuquerque using wind data over five years for the winter seasons. Compare 

with  Fig. 22 for the summer seasons, and note the fallout is transported generally toward the east in winter rather than toward the northwest an d west,  as is the  case in the summer. Dataand computations were supplied by Sandia Corporation, Albuquerque, N. Mex .

• Chama Raton *

Ro swelJ

0 20 40 60 80  100 1201 I I . I ! I . | , I | j

Miles

74

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FIGURE  24: PROBABILITIES FOR FALLOUT G A M MA RADIATION FROM 20-MT BURST

(SPRING SEASO N)

The probability contours inside which the infinity exposure dose from penetrating fallout

radiation would be 10 0  r or more were computed for a 20-Mt surface burst (1 0 M t fission yield)

at Albuquerque using wind data over five years for the spring seasons. Note that in general the

contour patterns for spring are similar to those for winter (Fig. 23) and fall (Fig. 2 5) . Data andcomputations were supplied by Sandia Corporation, Albuquerque, N. Mex.

—140

— 120

—100

-80

— 60

—40

— 20

—0  -

Shiprock

AztecCham

Raton

Gallup

'40 '20 '00 80 60 40 20

Roswell

20 40 60 80 100 120 140

Miles

7 5

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FIGURE 25: PROBABILITIES FOR FALLOUT GAMMA RADIATION  FROM 20-MT BURST 

(FALL SEASON)

The probability contours inside which the infinity exposure dose from penetrating fallout

radiation would be 100 r or more were computed for a 20-Mt surface burst (1 0 M t fission yield) 

at Albuquerque using wind data over five years for the fall seasons. Note that the contour pat

terns for fall are generally similar to those for winter  (Fig. 23 ) and spring (Fig. 24 ). Data and

computations were supplied by Sandia Corporation, Albuquerque, N. M ex .

I—140

Chama

Raron

Cimarron

Spr inger

-°-— — — - ,

12 0 100 80 6 0 40 20 20 40 60 80 100 120 1401 I I I I   I I I

Miles

76

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FIGURE 26: COMPUTED "MAXIMIZED" ISODOSE-RATE CONTOURS FOR 20-MT  BURST

"Maximized" isodose-rate contours from penetrating fallout radiation were computed for a

20-Mt surface burst (1 0 Mt fission yield) at Albuquerque using wind data over five years, 

showing contours for 100-, 300-, and I000-r/hr exposure-dose rates at H + 2 hr and 100-, 300-,

1000-, 3000-, and 10,000-r/hr exposure-dose rates at H + V   hr. The contours define the maxi

mal ranges at which the indicated dose  rates were predicted at least one day in five years, but

do not show conditions for any particular burst on any particular day, as illustrated in Figs. 12through 17 . The maximizing concept is useful for planning purposes in that it indicates from

real wind data that at least once in five years a given hazard from fallout radiation reached 

those ranges and directions from the target set out by the several contours. Data and compu

tations were supplied by Sandia Corporation, Albuquerque, N. Mex.

120 mi

100

80

60

40

20

0

20

40

60

80

100

120

140 mi

-|

N

-11

1

1

1

1

1

j1

COLORADO "*j— — — --— — — -- ———— -— — — _ , *" ir--

S I Shiprock Altec NEW MEXICO

) e •

Farmngton ,'

E

Gallup //?'' SonY,iaYo

/  /~   f j " " - ' it

%  Bel en

\\

t \ Bernardo"

\ \«

\ \

\\

**"\\

.Mogollon s%^ ^

•*%^

Truth or Consequences ^ ^

————— —————— —————l.1

•m°' ""~ • Raton</'"

' Cimarron•

• Springer

""' Note: ~v^,-""' (H+2) Dose  rate contour* "X

greater than 1,000 r/hr \are not shown. \

Los Alamos \ * Roye \

Sa nta Fe \

Pecos  9 im Vegas \

^^ (H-H/4) Pose  Rates: »

f"\\*\ 300 /h

BemaiiMk\V- - - - - 1 , 000 r/hr

f— _VL-t. ----10,000 r/hr —— — — — — —   ————

Mbuqu.ro.u-M I San fa Rosa

lt=/   ^   ^

— — — Vaughn. /

* / .Mountainair , ff>ft $umner

JCarrfzoza 

*Roswell

- Alamogordo ~""*~-~ i

1 1 ! 1 1 J i

1 2 0 m i 1 0 0 8 0 6 0 40 2 0 2 0 4 0 8 0 1 0 0 1 2 0 1 4 0 n

7 7

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FIGURE 27: COMPUTED "MAXIMIZED" ISODOSE C O N T O U R S FOR 20-MT BURST

"Maximized" isodose contours from penetrating fallout radiation were computed for a

20-Mt surface burst (10 Mt fission yield) at Albuquerque using wind data over five years show

ing contours for accumulated exposure doses of 100 , 1000 , and 10,000 r at H + 1 and H + 2 hr.

The contours show the maximal ranges over £   five-year period inside which the accumulated

dose was the stated amount or more. A s explained for Fig. 26 , the "maximized" contours arenot to be confused with contours computed for the wind pattern of a specified day . Computa

tions and data were supplied by Sandia Corporation, Albuquerque, N. Mex.

UTAH I ~ r

OKLAHOMA

Clayton • TEXAS

Tucumcar i I

Clovis

200m!L

i . •Silver C

L 1 0 0•4——I .LoKbburg

L 200 ml

V

50, , 1 , ,

•Domng

t0 50 tOO 150

__.—— _ t , . , , I , , , , 1 , , , , 1 , .

•Carltbod

•La s Cruces

NEW MEXICO

I TEXAS

Hobos*

200 mi

i

•——-—— ..

I MEXICO\

78

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FIGURE 28: COMPUTED "MAXIMIZED" INFINITY ISODOSE CONTOURS FOR 20-MT BURST

"Maximized" infinity isodose contours from penetrating fallout radiation were computed at

the nearer ranges for a 1-Mt  ( 2/   fission yield)  and a 20-Mt (V z fission yield) surface burst at

Albuquerque using wind data over five years for the spring seasons, showing contours for

exposure doses accumulated over infinite time of 5 000, 10,000, and 30,000 r for the  20-Mt 

burst and of 1000, 3000, and 6000 r for the 1-Mt burst. The contours set forth the maximal

ranges over a five-year period inside which the accumulated infinity dose was the statedamount or more. The reader is again cautioned not to confuse the contours with those appli

cable  to the wind pattern of a specified date. Computations and data were supplied by Sandia

Corporation, Albuquerque, N.  Mex.

Mil«s

79

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FIGURE 29: COMPUTED "MAXIMIZED" INFINITY ISODOSE CONTOURS FOR 20-MT BURST

"Maximized" infinity isodose contours from penetrating fallout radiation were computed

at  the near and farther ranges for a 20-Mt surface burst (1 0 M t fission yield) at Albuquerque

using wind  data over five years (all seasons), showing contours for infinity exposure doses of

100, 300, 1000, 3000, 10,000, and 30,000   r. The contours set forth the maximal  range and di

rection that might occur for the stated infinity dose over a five-year period. Thus, one cansay that at least once in five years  (1825 days) the indicated infinity doses were predicted to

reach the  ranges shown. The probability of the  maximal ranges shown occurring are quite remote, being numerically V i 8 2 5 = 0.00055. Too, there is some uncertainty concerning the sta

bility, range, and duration of the high winds at the greater altitudes. Even so, the figure servesto  emphasize, first, that some wind patterns are such as to carry fission debris over verygreat ranges, and, second, that planning protection and measures for minimizing exposure to

fallout radiation applicable to any  one area cannot be  realistically approached without thinking

of potential targets  in nearby states. Data and computations were supplied by Sandia Corporation, Albuquerque, N . M ex.

80

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BIBLIOGRAPHY

1. Auxier, J. A ., Evaluation of Residential Structures for Shielding Against Fallout Radiation,

pp , 148-151, Hearings Before the

Special Committee on Radiation of the Joint Committee on Atomic Energy, June 22-26,

1959 , U. S . Government Printing Office, Washington 25 , D . C ., 1959 .

2 * Auxier, J. A ., J. O. Buchanan, C . Eisenhauer, and H. E. Menker, Experimental Evaluation

of the Radiation Protection Afforded by Residential Structures Against Distributed Sources,

Civil Effects Test Operations, U S A E C Report CEX-58.1, Jan. 19, 1959 .3 . Benzinger, T., Physiological Effects of Blast in Air and Water, Chap. XIV-B,

Vol. II, pp . 1225-1259, U * S. Government Printing Office,

Washington 25, D. C ., 1950 .

4. Blizard, E. P. and J. M. Miller, Radiation Attenuation Characteristics of Structural C oncrete, Report ORNL-2193, Oak Ridge National Laboratory, Aug. 29 , 1958 .

5. Bowen, I . G., A. F. Strehler, and M. B. Wetherbe, Distribution and Density of Missiles from

Nuclear Explosions, Operation Teapot Report, WT-1168, Dec. 14, 1956 .

6. Bowen, I. G., D . R . Richmond, M. B. Wetherbe, and C . S . White, Biological Effects of Blastfrom Bombs. Glass Fragments as Penetrating Missiles an d Some of the Biological Implica

tions of Glass Fragmented by Atomic Explosions, U S A E C Report AECU-3350, Lovelace

Foundation for Medical Education and Research, June 18 , 1956 .7. Brooks, J. W ., F. H. Schmidt, R . C . Williams, and W. T. Ham, Jr., Effect of Skin Pigmenta

tion on Flash Burns in Human Volunteers, 8 : 125-128, (1958) .

8 . Butterfield, W. J. H., E . R . Drake Seager, J. R . B. Dixey, an d E. E. E. Treadwell, FlashBurns from Atomic Weapons. 1. Observations on Flash-burning of Human Subjects in the

Laboratory Using Infrared an d Predominantly White Light Sources,

103: 655-665 (1956).

9 . Byrnes, V. A ., Flash Blindness and Chorioretinal Burns Produced by Atomic Flash, J.168: 778-779 (1958).

10 . Callan, E. J., Concrete for Radiation Shielding, J. 25(11): 17-44 (1953) .

11. Celander, Hjordis, Carl-Johan Clemendson, U lf A. Ericsson, an d Holter I:son Hultman, A

Study on the Relation Between the Duration of a Shock Wave and the Severity of the Blast

Injury Produced by It, 33: 14-18 (1955).12 . Clemedson, Carl-Johan, An Experimental Study on Air Blast Injuries,

18, 61: 1-200 (1949).

13 . Cowan, Maynard, Jr., A Slide Rule Fallout Calculator, Technical Memo S C T M 177-57(51),

Sandia Corporation, Sandia Base, Albuquerque, N . Mex., Oct. 1, 1956 .14 . D e Haven, Hugh, Mechanical Analysis of Survival in Falls from Heights of 50 to 150 Feet,

2: 586-596 (1942).15. D e Haven, Hugh, Mechanics of Injury Under Force Conditions, 66: 264-268

(1944).16. Desaga, Hans, Blast Injuries, Chap. XIV-D, //,

Vol. II , pp. 1274-1293, U . S . Government Printing Office, Washington 25 , D . C., 1950 .17. Draeger, R. H., J. S . Barr, J. Y. Dunbar, W . W . Sager, and M. C. Shelesnyak, A Study of

Personnel Injury by "Solid Blast" and the Design and Evaluation of Protective Devices,

Naval Medical Research Institute Report N o. 1 ? Project X-517, Bethesda, Md., Mar. 30,

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18 . Eisenhauer, C . M ., Shielding from Fallout Radiation, pp . 151-163 of

Hearings Before the Special Committee on Radiation

of the Joint Committee on Atomic Energy, June 22-26, 1959, U. S. Government Printing

Office, Washington 25, D . C ., 1959 .

19. Evans, E. I., J. W. Brooks, F. H. Schmidt, R . C . Williams, an d W. T. Ham, Jr., Flash

Burn Studies on Human Volunteers, 37: 280-297 (1955).

20. Fisher, R . B., P. L. Krohn, and S. Zuckerman, The Relationship Between Body Size and

the Lethal Effects of Blast, Ministry of Home Security Report B.P.C. 146/W.S.ll, Nov. 23,

1941 .

21. Fisher, R . B., P. L. Krohn, and S. Zuckerman, The Relationship Between Body Size andthe Lethal Effects of Blast, Ministry of Home Security Report R.D. 284, Dec. 10 , 1941 .

22. Gerstner, H. B., Military and Civil Defense Aspects of the Acute Radiation Syndrome inMan, Report AF-SAM-58-6, Air Force School of Aviation Medicine, Randolph Air Force

Base, Texas, July 1957.

23 . Gerstner, H. B., Acute Clinical Effects of Penetrating Nuclear Radiation, < /.

168 : 381-388 (1958),24 . Glasstone, Samuel, Ed., U. S . Government Printing Office,

Washington 25, D . C ., June 1957.

25. Gurdjian, E. S ., J. E. Webster, and H. L. Lissner, Studies on Skull Fracture with Particular

Reference to Engineering Factors, Am. 78 : 736-742 (1949).26 . Ham, W. T., Jr., H. Wiesinger, F. H. Schmidt, R . C . Williams, R . S . Ruffin, M. C . Shaffer,

and D . Guerry III , Flash Burns in the Rabbit Retina as a Means of Evaluating the Retinal

Hazard from Nuclear Weapons, Am. J. 46: 700-723 (1958) .

27. Journ£e, Relationship Between the Kinetic Energy of Bullets and the Seriousness of WoundsWhich They M ay Inflict, May 1907.

28 . Kinsman, Simon, Ed., Fredric D . Anderson, Richard S * Cleveland, Bennett L. Harless, and

Charles F. Henke, Public Health Service, U. S. Department

of Health, Education an d Welfare, Office of Technical Services, U. S. Department of C ommerce, Washington, D . C., January 1957.

29. Price, B. T., C . C . Horton, an d K. T. Spinney, Pergamon Press,London, 1957.

30. Richmond, D . R., R. V. Taborelli, I . G. Bowen, T. L. Chiffelle, F. G. Hirsch, B. B. Long-well, J. G. Riley, C . S . White, F. Sherping, V. C . Goldizen, J. D . Ward, M. B. Wetherbe,

V. R . Clare, M. L. Kuhn, an d R. T. Sanchez, Blast Biology A Study of the Primary and

Tertiary Effects of Blast in Open Underground Protective Shelters, Operation PlumbbobReport, WT-1467, June 30, 1959 .

31. Richmond, D . R., R . V. Taborelli, F. Sherping, M. B. Wetherbe, R . T. Sanchez, V. C.

Goldizen, an d C . S. White, Shock Tube Studies of the Effects of Sharp-rising, Long-duration

Overpressures on Biological Systems, U S A E C Report TID-6056, March 1959 .

32. Richmond, D . R., M. B. Wetherbe, R. V. Taborelli, T. L. Chiffelle, and C . S . White, The

Biologic Response to Overpressure. L Effects on Dogs of Five to Ten-second Duration

Overpressures Having Various Times of Pressure Rise, 28 : 447-460 (1957).33 . Ritchie, R, H. and G. S . Hurst, Penetration of Weapons Radiation: Application to the

Hiroshima-Nagasaki Studies, 390-404 (1959).34. Ruff, Siegfried, Brief Acceleration: Less than One Second, Chap. VI-C,

//, Vol. I , pp, 584-597, U . S . Government Printing Office, Washington

25, D. C ., 1950 .35. Schardin, H., The Physical Principles of the Effects of a Detonation, Chap. XTV-A,

Vol. II, pp. 1207-1244, U. S. Government Printing Office,Washington 25, D. C., 1950 .

36. Schwartz, M . S ., H. S . Soroff, E. Reiss, an d P. A. Curtis, A n Evaluation of the Mortalityand the Relative Severity of Second- an d Third-degree Injuries in Burns, Research Report

MEDEW-RS-12-56, U. S. Army Medical Research Unit, Brooke Army Medical Center, FortS am Houston, Texas, December 1956.

37. Smith, Byron and William F. Regan, Jr., Blow-out Fracture of the Orbit,44: 733-739 (1957).

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CIVIL EF F ECT S T EST OPERATIONS R E P O R T S E R I E S (CEX)

Through its Division of Biology an d Medicine an d Civil Effects Test Opera

tions Office, the Atomic Energy Commission conducts certain technical tests,

exercises, surveys, and research directed primarily toward practical applica

tions of nuclear effects information an d toward encouraging better technical,

professional, and public understanding and utilization of the vast body of facts

useful in the design of countermeasures against weapons effects. The activities

carried out in these studies do not require nuclear detonations.A complete listing of all the studies no w underway is impossible in the

space available here,. However, the following is a list of all reports available

from studies that have been completed. A ll reports listed are available from

the Office of Technical Services, Department of Commerce, Washington 25,

D . C,, at the prices indicated.

CEX-57.1 The Radiological Assessment an d Recovery of Contaminated

($0.75) Areas, Carl F. Miller, September 1960.

CEX-58.1 Experimental Evaluation of the Radiation Protection Afforded by

($2.75) Residential Structures Against Distributed Sources, J. A . Auxier,

J. O. Buchanan, C . Eisenhauer, an d H. E. Menker, January 1959.

CEX-58.2 The Scattering of Thermal Radiation into Open Underground

($0.75) Shelters, T. P. Davis, N. D . Miller, T. S. Ely, J. A . Basso, an d

H. E. Pearse, October 1959 .

CEX-58.7 A E C Group Shelter, A E C Facilities Division, Holmes & Narver,

($0.50) Inc., June 1960 .

C EX-59.1 A n Experimental Evaluation of the Radiation Protection Afforded

($0.60) by a Large Modern Concrete Office Building, J. F. Batter, Jr.,

A . L. Kaplan, and E. T. Clarke, January I960.

C EX-59.13 Experimental Evaluation of the Radiation Protection Afforded by

($0.50) Typical Oak Ridge Homes Against Distributed Sources, T. D .

Strickler and J. A , Auxier, April 1960 .

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