by John Moore
May 26, 2009
from
TyniVitalSystems Website
This page holds a few
misc. facts about nuclear weapons and radiation that may
be surprising to many. |
Terrorist Related Information
"Suitcase Nukes"
-
The US produced, and for many years
deployed "Atomic Demolition Munitions." The
Medium Atomic Demolition
Munition (MADM) produced 1-15 kilotons of
yield, and weighed 400 pounds. The
Special Atomic Demolition Munition
(SADM) yielded .01-1 kilotons and weighed only 163
pounds.
-
The smallest nuclear weapon the US
produced was the "Davy Crockett" - a recoilless rifle round. It
weighed about 51 pounds, was 16 inches long and 11 inches in
diameter. It produced a variable yield of up to 1 kiloton.
-
An excellent discussion of this
issue is
here.
-
The Soviets supposedly produced
"suitcase nukes" and there is no reason to doubt this assertion.
Former Soviet General Ledbed has asserted that a number of these
are not accounted for. There are reasons, however, to doubt his
assertions given his political position. Interestingly, Ledbed
was recently killed in a helicopter crash.
-
The Soviets supposedly produced
"suitcase nukes" and there is a US DOE estimate that only 4kg of
Plutonium is necessary to make a fission weapon. Some believe
that only 1kg is needed.
Basic Nuclear Weapons
Engineering
-
See
Nuclear Weapons FAQ for primary
reference material.
-
All known nuclear weapons require
the fission of Uranium (235 or 233) or Plutonium 239. An "atomic
bomb" (fission weapon) uses the fission energy directly, while a
"hydrogen bomb" (thermonuclear weapon) uses fission to ignite a
fusion reaction, achieving much higher energy release. In
theory, there is no limit to the power of a fusion bomb. There
has been speculation that it is possible to create useful fusion
weapons without a uranium trigger, but no reliable unclassified
information indicates that this is true, and there is a
difficult physical principle to overcome.
-
Uranium consisting of unnaturally
high amounts of isotopes 233 and 235 is called enriched uranium.
Uranium is a common element on earth, but U-233 and U-235
constitute small percentages of it (<1%) and are always found
mixed with the less useful U-238.
-
Fission is the process whereby an
atom's nucleus splits, releasing a large amount of energy. In a
simple fission weapon, fission occurs when a neutron is absorbed
by a nucleus, causing it to be highly unstable, at which point
the nucleus splits, releasing a large amount of energy and more
neutrons. This only occurs easily in a few isotopes (in Uranium,
235 or 233).
-
A chain reaction occurs because the
fission of a nucleus releases additional neutrons, which can
then cause fission in more nuclei.
-
Critical mass is the amount of
fissile material needed for a chain reaction to become
self-sustaining. This means that for each neutron released in
the material, on average one more neutron will be released as a
result. The critical mass is a factor not just of the type and
amount of material, but also its instantaneous density and
geometry. In other words, a mass of plutonium might not be
critical until it is rapidly and highly compressed by high
velocity "implosion."
-
Fission weapons explode when the
fissile material is suddenly placed in a configuration
significantly greater than the critical mass - a state of supercriticality. If critical mass is reached too slowly, the
weapon will explode with greatly reduced energy, possibly simply
melting.
-
When a weapon has reached
supercriticality, it still may not explode unless a neutron
passes into the core. Since a high explosive implosion maintains
criticality for only a few microseconds, a neutron flux
generator may be required to guarantee this.
-
The easiest weapon to build uses a
large amount (tens of kilograms) of enriched uranium. Because
uranium releases neutrons at a very low rate, the weapon can use
a relatively long "assembly time" to reach supercriticality. One
design uses a sphere with a cylindrical hole in it, and a "gun"
to fire a cylinder of uranium into that hole. Until the cylinder
is inserted, both assemblies are well below critical mass, but
when the cylinder is inserted, the mass rapidly rises to
supercriticality. A neutron randomly released by the material
during this process triggers the chain reaction. This weapon is
so simple that the US used one against Nagasaki without ever
testing the design. These weapons tend to be fairly large and
inefficient, although the design was used in a US nuclear
artillery shell.
-
A plutonium based weapon cannot use
the "gun" approach, because plutonium releases too many
neutrons, which would cause the chain reaction to start long
before the mass was supercritical enough to cause a large
explosion. Hence plutonium weapons require assembly by
compressing a sphere or shell of plutonium very rapidly, using
high velocity explosives. This necessitates very high quality
explosives, a very precise machining of all parts, and an
electrical detonating system which can deliver very high energy
pulses to a number of detonators with great timing precision.
Hence plutonium based weapons are significantly harder to build.
The US tested one at Trinity Site before deploying another
against Nagasaki.
-
A uranium weapon can also use the
implosion approach, to achieve greater efficiency. However, in
this case it requires a neutron flux generator to assure that
enough neutrons flood the core during the maximal period of
compression that the chain reaction will start and the weapon
will be efficient.
-
Uranium weapons require the
production of enriched uranium (although it does not have to be
as highly enriched as is used in some power reactors). This is a
complex process because it requires the separation of isotopes
of the same element (which means they have the same chemical
behavior) and the isotopes have almost the same weight. Thus
multiple stages of gas diffusion, centrifuges or electromagnetic
(calutron) separation are required. This is inevitably a major
industrial project, and is likely to be detectable by
intelligence agencies. However, the centrifuge method can be
distributed, making it hard to spot. It is believed that Saddam
Hussein intended to use this approach once he was rid of UN
inspectors. Laser separation has also been used. In addition,
there may be new technologies that make enrichment much easier
to do or at least easier to conceal. Only a ton or so of natural
uranium is required to produce enough enriched uranium for a
weapon.
-
Plutonium weapons require the
production of highly pure plutonium. Because plutonium is a not
found in nature, it must be made in a nuclear reactor. Once
made, however, it is relatively easy to extract because it is
chemically different from the other elements in the mix,
although the extraction process must take place in an
environment made extremely radioactive by other elements mixed
with the plutonium.
-
Fusion weapons can be much more
powerful than fission weapons, but require a subtle and
difficult design. However, at least two different teams (Teller-Ulam
and Sakarov) independently discovered the same approach. Since
that time knowledge of fusion designs has spread through
espionage and possibly technology trades. The details of fusion
weapons will not be discussed here - see the Nuclear Weapons FAQ
for vastly more information.
Radiation Risk
- The Facts, not the Scare
Stories
-
Myth: Nuclear war would end
human life on earth through radiation.
Fact: If all of the nuclear
weapons in stock at the height of the cold war were detonated,
the average radiation dose per person is only 1/100th of a
lethal dose, and well below doses which can be shown to have
even long term effects (such as cancer).
-
Myth: Chernobyl caused or
will cause thousands of deaths.
Fact: The Chernobyl disaster
was the worst possible reactor disaster. It released an
extremely large amount of radiation into the environment (see
below). Even so, there have been no detectable increases in
death rates even among the most highly exposed population (other
than those who received extremely high doses fighting the fire,
and many of whom died as a result). The radiation levels of the
"highly radioactive" regions evacuated after the event are
significantly lower than the natural radiation level in many
parts of the world. Long term very sensitive genetic studies of
animals in the most highly exposed region have found no
abnormalities. There is no excess of three eared rabbits or 10
pound cockroaches around Chernobyl!
-
Myth: Fallout caused deaths
in Japanese nuclear bombings.
Fact: There was no
significant fallout in the vicinity of the Hiroshima and
Nagasaki bombings. All radiation injuries were a result of
immediate (first 1 minute) radiation.
-
The United States Transuranium and
Uranium Registries (USTUR), operated by Washington State
University, reports:
-
"The health effects from
plutonium, americium, and uranium intakes by humans, as
determined with USTUR data can be summarized in two
words, virtually none. A study of the causes of death of
USTUR organ donors has been completed. The study showed
that the vast majority of USTUR donors died from the
same diseases that have caused the deaths of most of the
U. S. population, heart disease, strokes, and cancers
not necessarily associated with radiation exposure. This
is in spite of the fact that the USTUR donors are a
biased population in that a number of donors volunteered
for the program after having been diagnosed with cancer.
The average age at death of USTUR registrants is 63
years (range between 25 and 91 years). The average age
of USTUR registrants who are still living is 73 years
(range between 30 and 93 years)."
-
The only human cases of significant
fallout exposure to humans (as of 1964, and outside of the USSR)
were in the Marshall Islands, after a U.S. test (CROSSROADS,
Bikini Atoll, 1946). The short term effects were skin burns,
nausea, and other symptoms typical of exposure to high radiation
doses. Even so, there was only one cancer (leukemia) likely
caused by the radiation, 18 years after exposure of a 1 year
old. Of the pregnancies in progress at time of exposure, there
was one miscarriage (no evidence for or against radiation
relationship). The rest produced healthy children. Not
surprisingly, there were a large number of cases of thyroid
problems, which lead to some reduced growth in children. A study
of the 40,000 military members who participated found no
scientific evidence of radiation induced cancers. References are
here. These results do not mean that fallout is harmless - far
from it, but they show that even radiation intense enough to
produce burns and nausea need not create a significantly
increased risk of cancer.
-
Almost all radioactivity in fallout
- even in a ground burst - comes from the fission products
themselves or transmutation of parts of the weapon. Thus air
bursts and ground bursts produce approximately the same amount
of radioactive products. However, ground bursts cause much more
of the radioactive debris to be deposited within a fallout
pattern, rather than distributed (and accordingly diluted and
decayed) across the entire planet.
-
There is
evidence that radiation is
beneficial and improves health (radiation hormesis) up to some
surprisingly high levels..
Blast Effects
More Technical Information
-
The blast effect is primarily
determined by the "overpressure" - given in English units in
PSI.
-
This effect at any distance is
proportional to the cube root of the weapons yield. Thus a 20
megaton bomb, which is large by today's standards, will affect
only 10 times the radius of a 20 kiloton bomb - which was the
yield at Hiroshima.
-
In Hiroshima, there was a 50%
survival rate 12 miles (200 meters) from ground zero. The bomb
went off at 1850 feet above ground zero with a yield of about
20kt. Concrete structures at ground zero survived.
-
In Hiroshima, there was only one
known case of burst eardrums among the survivors.
-
A human being can withstand up to
about 35PSI of peak overpressure from a nuclear blast (1%
fatality rate). Your mileage may vary. Thus a human will almost
always survive the blast overpressure at approximately the
following distances (slant range) from a blast according to the
following table:
Distance From Blast to Survive Blast Wave |
Yield |
Distance
(mi) |
Distance
(km) |
Comments |
20 kT |
.35 |
.56 |
Hiroshima
and Nagasaki |
600 kT |
1.1 |
1.8 |
Typical
Strategic US Nuke |
20 MT |
3.5 |
5.6 |
Very Big
Bomb |
|
-
The blast wave can, however, pick
people up and throw them. For a 165 pound standing person to be
thrown at 20 feet per second, the following table shows the
distance from the blast:
Distance From Blast to
be Thrown at 20 fps |
Yield |
Distance (mi) |
Distance (km) |
20kT |
1.06 |
1.75 |
600kT |
4.1 |
6.6 |
20MT |
16.8 |
27 |
|
|
|
Max Wind at
Distance from Blast |
Yield |
1 mi 1.6 km |
3 mi 4.8 km |
10 mi 16 km |
30 mi 48 km |
20kT |
200 mph 89 mps |
47 mph 21 mps |
5 mph 2 mps |
~0 |
600kT |
1000 mph 447 mps |
210 mph 94 mps |
51 mps 23 |
5 mps 2 |
20MT |
off scale |
1200 mph 536 mps |
195 mph 87 mps |
47 mph 21 mps |
|
-
The greatest danger from the blast
wave comes from destruction of structures and the conversion of
objects into missiles. The following tables gives the
destruction distance from various yields for a few kinds of
structures:
Window Breakage |
Yield |
Distance
(mi) |
Distance
(km) |
20kT |
3.2 |
5.1 |
600kT |
10 |
16 |
20MT |
32 |
51 |
Wood-frame Building Destruction |
Yield |
Distance
(mi) |
Distance
(km) |
20kT |
1.5
|
1.9 |
600kT |
4.8 |
7.7 |
20MT |
15 |
19 |
|
Multi-story
Brick |
Yield |
Distance (mi) |
Distance (km) |
20kT |
1.
|
1.6 |
600kT |
3.0 |
4.8 |
20MT |
10 |
16 |
Multi-story
Reinforced Concrete Offices |
Yield |
Distance (mi) |
Distance (km) |
20kT |
.5
|
.81 |
600kT |
1.3 |
2.1 |
20MT |
5 |
8.1 |
|
-
A ground burst produces a crater.
The following table shows crater sizes:
Crater Sizes |
Yield |
Width (feet) |
Width (m) |
Depth (feet) |
Depth (m) |
20kT |
633
|
193 |
80 |
24 |
600kT |
2112 |
643 |
211 |
64 |
20MT |
7392 |
2253 |
792 |
241 |
|
|
|
-
Historic Radiation Releases
Historic Radiation Releases (MegaCuries) |
Chernobyl |
7.3 MCi |
Hiroshima |
1.4 MCi |
Hanford (I-131 only) |
0.74 MCi |
Three Mile Island |
0.000015 MCi |
|
|
Nuclear
Physics Reference
-
The negative effects of radiation
can be divided into immediate effects (from very high dosages)
and long term effects (from lower dosages). Long term effects
are thought to be either the development of cancer, or genetic
damage passed on to offspring. However, there is no evidence
that low to moderate levels of radiation cause any long term
damage in humans, and some evidence that it may be beneficial
(radiation hormesis). Both long term effects would be a result
of damage to DNA - most likely nuclear DNA (as opposed to
mitochondrial DNA). However, the human cell experiences an
average of 70 million (7x107) DNA damages per year. Only 5 of
these are attributable to natural radiation. Even radiation much
higher than natural radiation would produce a negligible
percentage of the total DNA damage. The average natural human
dose is 2.2 mSv per year (see below for units). The lethal dose
is typically 3000 mSv - 5000 mSv.
-
Some elements of the following
tables of miscellaneous conversion factors are excerpted from
Nuclear Weapons Frequently Asked Questions
by Carey Sublette.
Units, Conversions
and Physical Constants |
Becquerel(Bq) |
1
Disintegration/Sec |
|
Curie (ci) |
3.7
1010 Disintegrations/Sec |
3.7
1010 Bq |
Rad |
.01
J/kg |
Radiation Exposure |
Sievert (Sv) |
100
REM (Grays*Q) |
Human Radiation Exposure |
REM |
Rads*RBE |
Human Radiation Exposure |
Gray(Gy) |
1
J/kg |
|
Gamma/Xray Roentgen (R) |
.94
erg/g |
|
Plutonum |
17
ci/g |
Half
Life: 24000 Years |
Depleted Uranium |
3.6
10-7 ci/g |
|
Natural Uranium |
7 10-7
ci/g |
contains .7% U235 |
Enriched Uranium |
7 10-7
ci/g |
|
1
Kiloton (kt) |
10^12 calories
4.19x10^12 Joules
2.62x10^25 MeV
fission of approx 57 g of material
1.16x10^t KWH<
|
|
1 eV |
1.602177x10^12 erg
11606 degrees K |
|
1
Bar |
10^5
pascals (nt/m^2)
.98687 atmospheres
14.5038 PSI |
|
Fission of U-235 or Pu-239 |
approx 17.5 kt/kg |
|
Fusion of pure deuterium |
82.2
kt/kg |
|
Total mass conversion |
21.47 Mt/kg |
|
|
References
Beneficial Radiation
And Regulations
by
Zbigniew
Jaworowski
Central Laboratory for Radiological
Protection
Ul. Konwaliowa 7, 03-194 Warsaw,
Poland
from
UniversitéP.M.Curie Website
recovered trough
WayBackMachine Website
Proceedings of ICONE 8 8th
International Conference on Nuclear Engineering April
2-6, 2000, Baltimore, MD USA, Paper No. 8790 |
Abstract
Administrative acceptance of the linear, no-threshold dose/effect
relationship (LNT) for radiological protection was convenient for
regulatory bodies, but is impractical, and inconsistent with
observations on beneficial effects of low doses and dose rates of
radiation, with a lack of increased malignancy and hereditary
disorders in inhabitants of areas with high natural radiation
background, and with a lack of genetic effects in progeny of
Hiroshima and Nagasaki survivors. Man-made contribution to the
average global individual radiation dose from all commercial nuclear
power plants, nuclear explosions and Chernobyl accident, amounts now
to about 0.4%, and from medical x-ray diagnostics 20% of the average
natural dose of 2.2 mSv per year. The natural dose is in many
regions of the world two orders of magnitude higher than the current
exceedingly low dose limit for population of 1 mSv per year. act
text here.
INTRODUCTION
A prompt criticality accident occurred in September last year at a
nuclear plant Tokaimura, Japan. Three workers absorbed potentially
lethal radiation doses of about 4500 to more than 20 000 milisieverts (mSv). One of them died on 83rd day after the accident.
Other was discharged from the hospital on 82nd day, and the third,
with skin lesions is successfully treated by skin grafts. Radionuclides produced in this accident by the short-term fission
reaction, entered the atmosphere, but no significant ground
contamination was found outside the plant boundary. Notwithstanding,
the local authorities evacuated 150 residents and urged another 310
000 to stay indoors. . Compared with other industrial accidents
occurring every day over the world, and which result in about 12 000
deaths per year in the United States alone, the Tokaimura incident
does not seem to have been very serious.
Nevertheless, it was described by the
media and by IAEA officials as "the world's third worst nuclear
accident behind Chernobyl and Three Mile Island", and the worst
nuclear accident in Japan, all of which is indeed correct. In Japan,
nuclear power has been in operation since 1965. Today, 35 years
later, almost 36% of its electric power is produced by 53 nuclear
reactors. One fatal victim during so long time just proves the
excellent safety of the vast nuclear industry in Japan. Every year
during the last decade, due to fatal accidents at work, Poland
suffered the loss of anywhere between 20 to 110 miners, to produce
about half of Japan's electric power output, almost exclusively by
burning coal.
Why then Tokaimura incident evoke such enormous media outcry? Why
did it provoke such a vehement reaction from the public and from
local and international authorities? Why had, for several days, the
Emergency Response Center of IAEA in Vienna, given reports on the
accident, sometimes five times daily, to all Permanent (national)
Missions to the IAEA, and to 213 National (emergency) Contact Points
all over the world? Why President Clinton ordered a safety survey of
all American nuclear facilities, as if what had occurred in Japan
could somehow extend to the United States?
Nothing like this occurs in any other
industry when three workers get electrocuted, or flashed by a hot
fumes, or die when a cloud of ammonia escapes from a factory or a
railway tank. Any minor, leak of radioactivity from a broken tube in
a reactor, even if completely innocent and bearing not relevance to
the overall safety of the plant, is trumpeted throughout the world,
and is used to direct mass emotions against the inherently safe and
environmentally friendly nuclear energy. What makes people demand
that nuclear industry to be a zero accident enterprise? Yet, at the
same time, the same people appear to willingly accept all other
kinds of man-made accidents, including the some 17 million deaths
estimated to be caused by cars since their invention. What causes
this paranoiac imbalance? An attempt to answer these questions is
the subject of this presentation.
The Chernobyl catastrophe resulted in vast quantities of radionuclides being released into the global atmosphere, which were
easy to measure even high in the stratosphere, and far away at the
South Pole. It was a godsend for anti-nuclear activists. Yet
according to estimates of the United Nations Scientific Committee on
the Effects of Atomic Radiation (UNSCEAR), one of the most
distinguished international authority in matters of ionizing
radiation, there were only 31 early death among the plant workers
and rescue operators, and no early death among the public.
Thirteen years after the accident, apart from an increase in thyroid
cancer registry (very likely due to increased screening rather than
a real increase in incidence), there is no evidence of a major
public health impact related to the ionizing radiation, and no
increase of overall cancer incidence or mortality that could be
associated with radiation exposure. There is no scientific proof of
any increase in other non-malignant disorders, genetic, somatic or
mental, that could be related to ionizing radiation from Chernobyl.
This UNSCEAR estimate is clearly quite different from what one finds
in most media, which prefer to cultivate mass radiophobia - an
irrational fear of radiation and all things nuclear. But who reads
UNSCEAR reports?
Chernobyl was the worst possible catastrophe of a badly constructed
nuclear power reactor: complete core meltdown, followed by free
dispersion of radionuclides in the atmosphere, and with an area of
lethal fallout, of only 0.5 km2, reaching up to 1800 meters from the
reactor. Nothing worse could happen with any reactor. It resulted in
comparatively minute death toll, amounting to about half of that of
each weekend's traffic in Poland. When the irrational rumble and
emotions of Chernobyl finally settle down, in the centuries to come,
this catastrophe will be seen as a proof that nuclear fission
reactors are a safe means of energy production. Several accidents at
hydroelectric, gas and coal energy production, and other industrial
catastrophes in the 20th century, each caused up to three orders of
magnitude greater death toll than the Chernobyl accident (Table 1).
In the highly contaminated regions of the former Soviet Union, from
which 270,000 people were evacuated and relocated, the 1986-95
average radiation doses from the Chernobyl fallout ranged between 6
and 60 mSv. By comparison, the world's average individual lifetime
dose due to natural background radiation is about 150 mSv. In the
Chernobyl-contaminated regions of the former Soviet Union, the
natural lifetime dose is 210 mSv - in many regions of the world it
is about 1000 mSv, and in the state of Kerala, India, or in parts of
Iran reaches 5000 mSv. Yet no adverse genetic, carcinogenic, or any
other deleterious effects of those higher, doses have been ever
observed among the people, animals, and plants that have lived in
those parts since time immemorial ; ; ; ; .
The forced evacuation of 270,000 people
from their, presumably, poisoned homes, and other forms of
overreaction of Soviet authorities (for example the famous "coffin
subsidy" - a monthly financial compensation), did not result in a
benefit, but instead induced some real harm: an epidemics of
psychosomatic disorders observed in the 15 million people of
Belarus, Ukraine and Russia, such as diseases of endocrinological
system, circulatory and gastrointestinal diseases, depression and
other psychological disturbances, headaches, sleeping disturbances,
difficulties in concentration, emotional instability, inability to
work and so on . The "coffin subsidy", which in impoverished Belarus
will total $86 billion by 2015 , for millions of recipients, each
time they sign a receipt, confirms that they are the "victims of
Chernobyl".
The psychosomatic disorders could not be attributed to the ionizing
radiation, but were assumed to be linked to the popular belief that
any amount of man-made radiation - even miniscule, close to zero
doses - can cause harm. This assumption, linear, no-threshold theory
(LNT) was accepted in the 1950s, arbitrarily, as the basis for
regulations on radiation and nuclear safety, now still in force. It
was under this assumption and regulations that the Soviet government
decided on the mass relocation of people from regions in which the
Chernobyl radiation dose was much smaller than natural radiation
background in many countries. This act of Soviet authorities
demonstrated not only absurdity of LNT, but also the harmful effects
of practical application of regulations based on this principle.
During the last three decades, the principles and regulations of
radiation protection have gone astray and have lead to exceedingly
prohibitive, LNT-derived standards and recommendations. Revision of
these principles, being now proposed by many scientists and several
organizations, was evoked both by an eye opening Chernobyl
experience, and by recent progress in radiobiology, genetics and
oncology.
Radiation carcinogenesis should no
longer be perceived as a straightforward process started by a random
hit by radiation to the DNA double strand in the cell. The
complexity of this process precludes the use of direct
proportionality even to estimate probability of the malignant cell
becoming a macroscopic, clinically verifiable tumor. After a total
malignant transformation, the cell has to divide some billions of
times, before a cancer is formed. Such transformed cells appear to
be distant from cancer by so many billions of iterative steps, that
their outcome cannot be predicted, as a matter of principle .
A great radiobiologist, the late Harald Rossi summarized the
situation as follows:
"It would appear...that radiation
carcinogenesis is an intricate intercellular process and that
the notion that it is caused by simple mutations in a
unicellular response is erroneous. Thus, there is no scientific
basis for the "linearity hypothesis" according to which cancer
risk is proportional to absorbed dose and independent of dose
rate at low doses" .
One of the factors responsible for these
winds of change is recognizing by many scientists that small doses
of radiation, like small doses of other physical or chemical agents,
may be beneficial for organisms, and evoke a stimulatory or hormetic
response, which is in direct opposition to the LNT. About 2000
scientific papers on radiation hormesis were published in the 20th
century. However, when in 1982 I proposed that UNSCEAR should review
and assess these papers, nobody seemed interested. Each following
year I had repeated this proposal in vain, until after Chernobyl, in
1987, it finally gained support from the representatives of France
and Germany. It took UNSCEAR some dozen years of deliberations
before in 1994 the Committee published its fundamental report ,
rubberstamping the very existence of phenomenon of hormesis.
It was difficult for the Committee to
overcome its own prejudices on radiation hormesis, and to produce a
balanced objective report. Along the way, the Committee rejected two
rather one-sided drafts of "hormesis document", but in 1990 also an
excellent document on "Hereditary Effects of Radiation", prepared by
a leading expert in the field, professor F. Vogel.
This last rejection demonstrated a
hesitating mood of the Committee, as the Vogel's paper showed lack
of genetic effects after Chernobyl accident, presented the existence
of hormetic effects in children of Hiroshima and Nagasaki survivors,
and the lack of any hereditary disorders both in these children, and
in inhabitants of high natural background radiation areas. The draft
of UNSCEAR 1994 "hormetic report" was prepared by
Dr. Hylton Smith,
then the Scientific Secretary of the ICRP, a body strongly
supporting LNT and rejecting hormesis.
However, working for a few years on this
report, Dr. Smith changed his initially negative approach to
radiation hormesis, and finely produced an excellent, unbiased
treatise on this yet unfathomed matter, demonstrating his scientific
integrity.
This report sparked in the radiation protection community a quasi
revolution, which is now gaining momentum, with some encouragement
from the chairman of ICRP, professor Roger Clarke .
NATURAL
AND MAN-MADE
The linear no-threshold hypothesis was accepted in 1959 by the
International Commission on Radiological Protection (ICRP) as a
philosophical basis for radiological protection . This decision was
based on the first report of the, then just established, UNSCEAR
committee. Large part of this report was dedicated to a discussion
of linearity and of the threshold dose for adverse radiation
effects. UNSCEAR's stand on this subject, more than forty years ago,
was formed after an in-depth debate, not however without any
influence of the political atmosphere and issues of the time.
Soviet, Czechoslovakian and Egyptian delegations to UNSCEAR strongly
supported the LNT assumption, using it as a basis for recommendation
of an immediate cessation of nuclear test explosions.
The then prevailing target theory and
the then new results of genetic experiments with fruit flies
irradiated with high doses and dose rates, strongly influenced this
debate. In 1958 UNSCEAR stated that contamination of the environment
by nuclear explosions increase radiation levels all over the world,
posing new and unknown hazards for the present and future
generations. These hazards cannot be controlled and "even the
smallest amounts of radiation are liable to cause deleterious
genetic, and perhaps also somatic, effects".
This sentence had an enormous impact in
the next decades, being repeated in a plethora of publications, and
taken even now as an article of faith by the public. However,
throughout the whole 1958 report, the original UNSCEAR view on LNT
remained ambivalent. At example, UNSCEAR accepted as a threshold for
leukemia a dose of 4000 mSv (page 42), but at the same time the
committee accepted the risk factor for leukemia of 0.52% per 1000
mSv, assuming LNT (page 115).
Committee quite openly presented this
difficulty, showing in one table (page 42) its consequences:
continuation of nuclear weapon tests in the atmosphere was estimated
to cause 60,000 leukemia cases worldwide if no threshold is assumed,
and zero leukemia cases if a threshold of 4000 mSv exists. In final
conclusions the UNSCEAR pinpointed this situation:
"Linearity has been assumed
primarily for purposes of simplicity", and "There may or may
not be a threshold dose. Two possibilities of threshold and
no-threshold have been retained because of the very great
differences they engender".
In the ICRP document of 1959 no such
controversy appears, LNT was arbitrarily assumed, and serious
epistemological problems related to impossibility of finding harmful
effects at very low levels of radiation {later discussed by and }
were ignored. Over the years the working assumption of ICRP of 1959
came to be regarded as a scientifically documented fact by mass
media, public opinion and even many scientists. The LNT principle,
however, belongs to the realm of administration and is not a
scientific principle.
In these early years the LNT assumption did not seem very realistic,
but was generally accepted because it simplified regulatory work.
The original purpose was to regulate the exposure to radiation of a
relatively small group of occupationally exposed persons, and it did
not involve exceedingly high costs. In the 1970s, however, ICRP
extended the LNT principle to exposure of the general population to
man-made radiation, and in the 1980s it extended LNT limiting the
exposure to natural sources of radiation . In the same document ICRP
recommended restriction of radiation exposure of members of the
public to 1 mSv per year, that is below the average annual global
natural radiation dose of 2.2 mSv, and many tens or hundreds of
times lower than the natural doses in many regions of the world.
Such an absurdly low limitation of
exposure was a logical consequence of administrative LNT assumption
from 1959. It made a false impression in the public that new
research steadily discovers a greater harmfulness of radiation,
which needs more protection, more money, and lower standards. In
fact nothing like this occurred. Since introduction of rational
standards in the 1930s, which were based on tolerance dose concept,
and were orders of magnitude higher than now, no deleterious effects
were found among those that observed them (Taylor, 1981).
This constant decreasing of standards, however, was less than
palatable to many scientists associated with radiation protection,
standing both on purely scientific and practical grounds. One of the
important factors in changing opinion of many scientists was finding
actual proportions between man-made and natural exposures. Data
published in the UNSCEAR documents clearly show that the average
individual global radiation dose in 1990 from nuclear explosions,
the Chernobyl accident, and commercial nuclear plants combined was
about 0.4% of the average natural dose of 2.2 mSv per year. In areas
of the former Soviet Union that were highly contaminated by
Chernobyl fallout, the average individual dose was much lower than
that in regions with high natural radiation.
The greatest man-made contribution to
radiation dose has been irradiation from x-ray diagnostics in
medicine, which accounts for about 20% of the average natural
radiation dose (Figure 1). From the medical point of view, it does
not matter whether ionizing radiation comes from natural or from
man-made sources: its nature is the same. We do not observe any
adverse effects of irradiation from Mother Nature's sources: no
increase of cancers and hereditary disorders was ever found in
natural high radiation areas. The concern about large doses, such as
absorbed by three workers in Tokaimura or by 28 fatal radiation
victims in Chernobyl, is obviously justified. But should we spend
enormous funds to protect people against radiation corresponding to
tiny fractions of natural doses, only because humans make them?
Few billion years ago, when life on Earth began, the natural level
of ionizing radiation was about three to five times higher than it
is now . At the early stages of evolution, increasingly complex
organisms developed powerful defense mechanisms against adverse
effects of this radiation, and of all kinds of environmental
factors, for example against toxicity of oxygen and other
innumerable inorganic and organic toxins, and dangerous physical
agents, including the whole range of radiation energy spectrum.
Living organisms developed not only protective mechanisms against
these environmental agents, but they learned how to use them to
their advantage.
We see this readily in the case of
visible light and UV radiation. UV radiation belongs to the ionizing
part of the spectrum. It is rather doubtful that other types of
ionizing radiation were excluded from this evolutionary adaptive
process. The phenomenon of radiation hormesis observed in man, and
in animals argues against such exclusion. On the other hand, that
the evolution proceeded for so long is proof of the effectiveness of
living things' defenses against environmental agents, including
ionizing radiation.
The adverse effects of ionizing radiation, such as mutation and
malignant change, originate in the cell nucleus, where the DNA is
their primary target. Other adverse effects - which lead to acute
radiation sickness and premature death in humans, also originate in
the cell, but outside its nucleus. For them to take place requires
radiation doses thousands of times higher than those from natural
sources. A nuclear explosion or a cyclotron beam could deliver such
a dose; so could a defective medical or industrial radiation source
- Tokaimura and Chernobyl are two examples. An artificial
distinction between these two types of effects:
(1) starting in the DNA
of the cell nucleus
(2) outside the nucleus
was made by introducing terms of "stochastic effects" for
late malignant and hereditary changes, and "deterministic
effects" for early acute changes and cataracts
Medicine does not recognize such a
distinction. In fact, it was a tacit introduction of the LNT
thinking template into radiation protection. By definition,
stochastic (probabilistic) effect is "an all-or nothing effect, the
severity of which does not vary with dose" , and which distinguishes
them from "deterministic" effects, the severity of which increases
with dose.
However, both notions: stochastic and deterministic effects seem
rather empty and obsolete, in view of the new information on
mechanisms of carcinogenesis and genetics. The lack of dose related
severity in stochastic effects - the main difference between them
and deterministic effects, is simply not true. As demonstrated by
many radiogenic cancers in man and in experimental animals show
greater histologic and clinical malignancy after high radiation
doses than after smaller ones. Also latency time is shortened when
the dose increases, so the malignant tumors can have more time to
develop during a lifetime.
According to recent studies, by far the most DNA damage in humans is
spontaneous and is caused by thermodynamic decay processes and by
reactive free radicals formed by the oxygen metabolism. Each
mammalian cell suffers about 70 million spontaneous DNA-damaging
events per year . More recent measurements of steady state oxygen
free radical damages to DNA (Helbock et al., 1998) and their repair
rates (Jaruga, Dizderoglu, 1996) demonstrate about 350 million
metabolic DNA oxidamages per cell per year. Only if armed with a
powerful defense system could a living organism survive such a high
rate of DNA damage.
An effective defense system consists of mechanisms that repair DNA,
and other homeostatic mechanisms that maintain the integrity of
organisms, both during the life of the individual and for thousands
of generations. Among those homeostatic mechanisms are antioxidants,
enzymatic reactions, apoptosis (suicidal elimination of changed
cells), immune system removal of cells with persistent DNA
alterations, cell cycle regulation, and intercellular interactions.
Ionizing radiation damages DNA also, but at a much lower rate. At
the present average individual dose rate of 2.2 mSv per year,
natural radiation could be responsible for no more than about 5
DNA-damaging events in one cell per year. Why with a background of
70 million spontaneous DNA damages per cell per year, should we
protect people against 2.3 DNA damages per cell per year, expected
from 1 mSv annual dose limit recommended by ICRP? Though spontaneous
repairing of double strand break damages of DNA occurs rarely
compared to their occurrence in radiation damage, spontaneous oxygen
metabolism induces about 1000 timeas as many double strand breaks as
background radiation (Stewart, 1999). In this perspective even a
limit permitting for 200 DNA damages per cell per year, or 100 mSv
per year, would be proper.
As compared with other noxious agents, ionizing radiation should be
regarded as rather feeble. The safety margin for ionizing radiation
is much larger than for many other agents present in the
environment, e.g. thermal changes, plant and animal poisons, or
heavy metals. For example, a toxic level of lead in blood is only 3
times higher than its "normal" level. A lethal dose of ionizing
radiation delivered in one hour - which for an individual human is
3000 to 5000 mSv - is a factor of 10 million higher than the average
natural radiation dose received in the same time (0.00027 mSv).
Nature seems to have provided living
organisms with an enormous safety margin for natural levels of
ionizing radiation - and also, adventitiously, for man-made
radiation from controlled, peacetime sources. Conditions in which
levels of ionizing radiation could be noxious do not normally occur
in the biosphere, so humans required no radiation-sensing organ and
none evolved, although all species have always been immersed in the
sea of radiation ever since life began.
WHY
RADIOPHOBIA?
If radiation and radioactivity, though ubiquitous, are so innocuous
at normal levels, why do they cause such universal apprehension?
What is the cause of radiophobia, an irrational fear that any level
of radiation is dangerous? Why have radiation protection authorities
introduced a dose limit for the public of 1 mSv per year, which is
less than half the average dose rate from natural radiation, and
less than 1% of the natural dose rates in many areas of the world?
Why do the nations of the world spend many billions of dollars a
year to maintain this standard ? In a recent paper I proposed some
likely reasons :
-
The psychological reaction to
devastation and loss of life caused by the atomic bombs dropped
on Hiroshima and Nagasaki at the end of World War II.
-
Psychological warfare during the
cold war that played on the public's fear of nuclear weapons.
-
Lobbying by fossil fuel industries.
-
The interests of radiation
researchers striving for recognition and budget.
-
The interests of politicians for
whom radiophobia has been a handy weapon in their power games
(in the 1970s in the USA, and in the 1980s and 1990s in eastern
and western Europe and in the former Soviet Union).
-
The interest of news media that
profit by inducing public fear.
-
The interest of "greens" that profit
by inducing public fear.
The assumption of a linear, no-threshold
relationship between radiation and biological effects (LNT). In
addition, a very important factor was:
Complaisance of nuclear industry
leadership, paralyzed by anti-nuclear propaganda. Intimidated
industry accepted irrational standards, and did not develop
research programs to check the validity of LNT.
During the past five decades nuclear
weapons were regarded as a deterrent, and the countries that possess
them wished to make radiation and radioactivity seem as dreadful as
possible. Therefore, national security agencies seldom correct even
the most obviously false statements, such as often voiced:
"Radiation from a nuclear war can annihilate all mankind, or even
all life", or (the ever authoritative International Herald Tribune)
"200 grams of plutonium could kill every human being on Earth" .
The facts say otherwise. According to UNSCEAR reports, between 1945
and 1980, the 541 atmospheric nuclear tests, injected into the
global atmosphere about 3000 kilograms of plutonium (that is, almost
15 000 supposedly deadly 200-gram doses), yet lo and behold: somehow
we are still alive! (Try to publish this in the International Herald
Tribune: no way).
According to UNSCEAR data, from all these 541 atmospheric explosions
with a total energy yield of 440 megatons of TNT, we accumulated
between 1945 and 1998, an average individual radiation dose of about
1 mSv, what is less than 1% of the dose from natural sources over
the same period. In the heyday of atmospheric testing, 1961 and
1962, there were 176 atmospheric explosions, with a total energy
yield of 84 megatons. The average individual dose accumulated from
the fallout between 1961 and 1964 was about 0.35 mSv.
At its cold war peak of 50 000 weapons,
the global nuclear arsenal had a combined potential explosive power
of about 13 000 megatons, which was only 30 times larger than the
megatonnage already released in the atmosphere by all previous
nuclear tests. If that whole global nuclear arsenal had been
deployed in the same places as the previous nuclear tests, the
average individual would have received a lifetime radiation dose
from the global fallout of about 30 to 55 mSv, a far cry from the
short-term dose of 3000 mSv that would kill a human.
For several decades, humanity had lived under the gloomy shadow of
imminent nuclear annihilation. This had extremely negative influence
not only on public perception of radiation and nuclear energy, but
induced a cultural change: an distrust of science, rejuvenation of
irrational apocalyptic mythologies, and even aversive approach to
civilization, the fruit of toil and sweat of ourselves and of our
forefathers.
HIROSHIMA, NAGASAKI AND LNT
The survivors of the atomic bombing of Hiroshima and Nagasaki who
received instantaneous radiation doses of less than 200 mSv have not
suffered significant induction of cancers . Among 59 539 inhabitants
of these two cities that absorbed doses up to 1990 mSv, 119 persons
died between 1950 and 1985, due to leukemia, i.e. about 0.006% per
year, and 4.319 persons died due to all other cancers, i.e. 0.2% .
According to the Polish Cancer Registry data, in 1993 0.006% people
died in Poland due to leukemia, and about 0.2% due to all other
cancers . This comparison shows that with doses of up to near 2000 mSv we should not expect any detectable epidemic of malignances.
Among the bomb survivors irradiated with
doses lower than 150 mSv mortality caused by leukemia was lower
(although statistically not significant) than among the
non-irradiated inhabitants of two Japanese cities . A slight, but
non significant, decrease in overall non-cancer mortality among bomb
survivors exposed to low and intermediate dose can also be seen in
the data of Atomic Bomb Casualty Commission and the Radiation
Effects Research Foundation . So far, after 50 years of study, the
progeny of Japanese survivors who were exposed to these and much
higher, near lethal doses had not developed any adverse genetic
effects .
Until recently, such findings from the study of A-bomb survivors has
been consistently ignored. In place of the actual findings has been
the theory of linear no-threshold (LNT), which presumes that the
detrimental effects of radiation are proportional to the dose, and
that there is no dose at which the effects of radiation are not
detrimental. LNT theory played an important role in effecting first
a moratorium and then a ban on atmospheric nuclear tests. But
otherwise its role was mostly negative, inducing worldwide fear of
radiation and effective strangulation of development of nuclear
energy systems in many countries, including the United States. My
own country, Poland, spent billions of dollars on construction of
its first nuclear power station, only to abandon the project after
politically motivated manipulation of the public opinion by means of
the LNT theory.
The mechanism of inducing fear is quite
simple. For example, one calculates, very exactly, that 28 000
people would die of Chernobyl-induced cancers over the next 50
years, and news media trumpet this, or much greater values all over
the world, now and again, and ad nauseam. The frightening death toll
was derived by multiplying the trifling Chernobyl doses in the
Northern Hemisphere, including Canada and the United States (0.0046 mSv per person) by the vast number of people leaving there and by a
cancer risk factor based on epidemiological studies of 75 000 atomic
bomb survivors in Japan .
But the A-bomb survivor data are
irrelevant to such estimates, because of the difference in the
individual doses and dose rates. A-bomb survivors were flashed
within about one second by radiation doses at least 50 000 times
higher than dose which US inhabitants will ever receive, over the
period of 50 years, from the Chernobyl fallout.
We have reliable epidemiological data for a dose rate of, say, 6000
mSv per second in Japanese A-bomb survivors. But there are no such
data for human exposure at a dose rate of 0.0046 mSv over 50 years
(nor will there ever be any). The dose rate in Japan was larger by 2
x 1015 than the Chernobyl dose rate in the USA. Extrapolating over
such a vast span is neither scientifically justified nor
epistemologically acceptable. It is also morally suspect .
An offspring of the LNT assumption is the concept of dose
commitment, introduced in the early 1960, and of collective dose.
Dose commitment reflected the great concern, at that time, that
harmful hereditary effects could be induced by fallout from nuclear
tests. The concern was so great, that according to definition, dose
commitment values were to be calculated for periods of time ending
in the infinity. In later years, the individual dose commitments,
and collective dose commitments, also for some truncated periods,
were calculated mainly for exposures from nuclear power. For
example, UNSCEAR calculated 205 000 man Sv for the next 10 000 years
from power reactors and reprocessing plants, 600 000 man Sv from
Chernobyl fallout in the Northern Hemisphere for eternity, and 650
000 000 mSv for the world's population from only past 50 years of
exposure to natural radiation.
These large values, terrifying as they
are to the general public, provide society with no relevant
biological or medical information. Rather, they create a false image
of the imminent danger of radiation, with its all actual negative
social and psychosomatic consequences. But why to stop at 50 years
calculating dose commitments for natural radiation, when for
man-made radiation, one make estimates over infinite time? For
example, the individual dose commitment, supposedly accumulated over
the past 130 000 years of existence of the modern Homo sapiens, and
calculated for now living average human, is 286 000 mSv, i.e. about
hundred short term lethal doses.
Each of us is burdened with this or
similar value of dose commitment. Do these values represent anything
real, or are they just figments of scholastic fantasies? What are
the medical effects of these enormously high doses? I proposed in a
recent paper, that the intellectually invalid concepts of
collective dose and dose commitment be hacked off with William of Occam's razor.
Acknowledgments
I am indebted to Dr. Michael
Waligórski for stimulating discussion and comments.
References
-
Ageeva, L.A., 1996.
Socialno-psikhologicheskie posledstviya Chernobylskoi katastrofy
dlya naseleniya Belarusi i ich smyagchenie, International
Conference: One Decade after Chernobyl: Summing up the
Consequences of the Accident. Book of Extended Synopses. IAEA,
Vienna, pp. 63-67, (in Russian).
-
Billen, D., 1994. Spontaneous DNA
damage and its significance for the "negligible dose"
controversy in radiation protection. BELLE Newsletter, 3(1):
8-11.
-
Cheriyan, V.D., Kurien, C.J., Das,
B., Ramachandran, E.N., Kurappasamany, C.V., Thampi, M.V.,
George, K.P., Kesavan, P.C., Koya, P.K.M., Chauhan, P.S., 1999.
Genetic monitoring of the humann population from high-levelo
natural radiation areas of Kerala on the South West Coast of
India. II. Incidence of numerical and structural chromosomal
aberrations in the lymphocyte of newborns. Radiation Research,
152: S154-S158.
-
Clarke, R., 1999. Control of
low-level radiation exposure: time for a change? Journal of
Radiological Protection, 19(2): 107-115.
-
Cohen, B.L., 1992. Perspectives on
the cost effectiveness of life saving. In: J.H. Lehr (Editor),
Rational Readings on Environmental Concerns. Van Nostrand
Reinhold, New York, pp. 461-473.
-
Cohen, B.L., 1998. The cancer risk
from low-level radiation. Radiation Research, 149 (May):
525-528.
-
Filyushkin, I.V., 1996. The
Chernobyl accident and the resultant long-term relocation of
people, 71(1): 4-8.
-
Goldman, M., Catlin, R.J. and
Anspaugh, L., 1987. Health and environmental consequences of the
Chernobyl Nuclear Power Plant accident. DOE/RR-0232, U.S.
Department of Energy, Washington, D.C.
-
Helbock, H.J., Beckman, K.B.,
Shigenaga, M.K., Walter, P.B., Woodall, A.A., Yeo, H.C., Ames,
B.N., 1998. DNA oxidation matters: The HPCL-electrochemical
detection assay of 8-oxo-deoxyguanosine and 8-oxo-guanine.
Proceedings of the National Academy of Sciences, USA, 96:
288-293.
-
Hezir, J.S., 1995. Statement at
EPA's Public Hearing on the Proposed Recommendations for Federal
Radiation Protection Guidance for Exposure of the General
Public. February 22-23, 1995, Washington, D.C.
-
IAEA-ERC, 1999. Information
Adfvisory concerning incident in Japan No. 8, International
Atomic Energy Agency. Emergency Responce Centre, Vienna,
Austria.
-
ICRP, 1959. Recommendations of the
International Commission on Radiological Protection. ICRP
Publication No. 1. Pergamon Press, London.
-
ICRP, 1977. Recommendations of the
International Commission on radiological Protection. ICRP
Publication No. 26. Pergamon Press, Oxford.
-
ICRP, 1984a. Protection of the
public in the event of major radiation accidents: Principles for
planning. ICRP Publication 40. Pergamon Press, Oxford.
-
ICRP, 1984b. Principles for limiting
exposure of the public to natural sources of radiation. ICRP
Publication No. 39. Annals of ICRP, 14(1): i-vii.
-
IHT, 1996. Bhopal victims protest
ruling- potentially lethal. Nov. 27, 1996.
-
Ilyin, L.A., 1995. Chernobyl: Myth
and Reality. Megapolis, Moscow.
-
Jaikrishan, G. et al., 1999. Genetic
monitoring of the human population from high-level natural
radiation area of Kerala on the South West Coast of India. I.
Prevalence of congenoital malformations in newborns. Radiation
Research, 152: S149-S153.
-
Jaruga, P. and Dizdaroglu, M., 1996.
Repair of products of oxidative DNAAA base damage in human
cells. Nucleic Acid Research, 24: 1389-1394.
-
Jaworowski, Z., 1996. Chernobyl in
Poland: The first few days, ten years later. In: A. Bayer, A.
Kaul and C. Reiners (Editors), Zehn Jahre nach tschernobyl, eine
Bilanz. Gustav Fisher, Stuttgard, Munich, Germany, pp. 281-300.
-
Jaworowski, Z., 1998. All
Chernobyl's victims: A realistic assessment of Chernobyl's
health effects. 21st Century Science and Technology, 11(1):
14-25.
-
Jaworowski, Z., 1999. Radiation risk
and ethics. Physics Today, 52(9): 24-29.
-
Jaworowski, Z., Hoff, P., Hagen, J.O.
and Maczek, W., 1997. A highly radioactive Chernobyl Deposit in
a Scandinavian glacier. Journal of Environmental Radioactivity,
35(1): 91-108.
-
Karam, A., 1999. The evolution of
the Earth's background radiation field over the past four
billion years. SSI News, 7(1): 12-15.
-
Kesavan, P.C., 1996. Indian research
on high levels of natural radiation: pertinent observations for
further studies. In: L. Wei, T. Sugahara and Z. Tao (Editors),
High levels of Natural Radiation 1996. Radiation Dose and Health
Effects. Elsevier, Amsterdam, Beijing, China, pp. 111- 117.
-
Kondo, S., 1993. Health Effects of
Low-level Radiation. Kinki University Press, Osaka, Japan, 213
pp.
-
Koning, H., 1996. Potentially
lethal. International Herald Tribune (27 November, 1996).
-
Lewis, C., 1999. Japanese
criticality accident rated level four on INES scale. The World's
Nuclear News Agency, No. 399/99/A(1 October).
-
Nair, K.M.K. Nambi, K.S.V., Amma,
N.SSS., Gangadharan, P., Jayadevan, S., Cherian, V., Reghuran,
K.N., 1999. Population study in the high natural background
radiation area in Kerala, India. Radiation Research, 152:
S145-S148.
-
NCRP, 1995. Principles and
Aplication of Collective Dose in Radiation Protection. NCRP
Report No. 121, National Council on Radiation Protection and
Measurements, Bethesda, Maryland.
-
Rolevich, I., Kenik, I.A., Babosov,
E.M. and Lych, G.M., 1996. Report of the Republic of Belarus.
Ten years after Chernobyl: Ecological consequences of the
accident at the CAPS in the Republic of Belarus. One decade
after Chernobyl: summing up the radiological consequences of the
accident, Vienna, Austria, (manuscript).
-
Sankaranarayanan, K., 1997. Recent
advances in genetic risk estimation. Lecture presented at 46th
session of UNSCEAR, UNSCEAR document 46/10, 18 June, 1997.
-
Sasaki, Y., 2000. Letter of
Professor Yasuhito Sasaki, Director General of the National
Institute of Radiological Sciences, Anagawa, Japan to Zbigniew
Jaworowski, of January 20, 2000.
-
Shimizu, Y., Kato, H., Schull, W.J.
and Hoel, D.G., 1992. Studies of the mortality of A-bomb
survivors. 9. Mortality, 1950-1985: Part 3. Noncancer mortality
based on the revised doses (DS86). Radiation Research, 130:
249-266.
-
Shimizu, Y., Kato, H., Schull, W.J.,
Preston, D.L., Fujita, S., Pierce, D.A., 1989. Studies of
mortality of A-bomb survivors. 9 Mortality, 1950-1985: Part 1.
Comparison of risk coeficients for site-specific cancer
mortality based bon the DS86 and T65DR shielded kerma and organ
doses. Radiation Research, 118: 502-524.
-
Sohrabi, M., 1990. Recent
radiological studies of high level natural radiation areas of
Ramsar. In: J.U.A. M. Sohrabi, and S.A. Durrani (Editor), High
Levels of Natural Radiation. IAEA, Ramsar, Iran, pp. 39-47.
-
Stewart, R.D., 1999. On the
complexity of the DNA damages created by endogenous processes.
Radiation Research, 152:1101-1102.
-
Taylor, L.S., 1981. Technical
accuracy in historical writing. Health Physics, 40: 595-599.
-
UNSCEAR, 1958. Report of the United
Nations Scientific Committee on the Effects of Atomic Radiation,
United Nations, New York.
-
UNSCEAR, 1994. Annex B: Adaptive
responses to radiation in cells and organisms. Sources and
Effects of Ionizing Radiation. Report of the United Nations
Scientific Committee on the Effects of Atomic Radiation. United
Nations, New York.
-
UNSCEAR, 1999. Exposures and Effects
of the Chernobyl Accident. A/AC.82/R.599, United Nations
Scientific Committee on the Effects of Atomic Radiation.,
Vienna.
-
Walinder, G., 1987. Epistemological
probles in assessing cancer risks at low radiation doses. Health
Physics, 52(5): 675-678.
-
Walinder, G., 1995. Has radiation
ptotection become a health hazard? The Swedish Nuclear Training
& Safety Center, Nykoping, 126 pp.
-
Weinberg, A.M., 1972. Science and
trans-science. Minerva (London), 10: 209-222.
-
Zatonski, W. and Tyczynski, J.,
1996. Cancer in Poland in 1993, The Maria Sklodowska-Curie
Memorial Cancer Center and Institute of Oncology, Warsaw.
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