Det danske Fredsakademi
Kronologi over fredssagen og international politik 21. februar
2005 / Time Line February 21, 2005
Version 3.5
20. Februar 2005, 22. Februar 2005
02/21/2005
The Invisible War: Depleted Uranium and the Politics of
Radiation 2000
The Honorable Jim McDermott, Congressman
Washington State 7th Congressional District
1809 7th Avenue
Suite 1212
Seattle, WA 98101-1399
(206) 553-7170
(206) 553-7175 FAX
Re: Declassified 1943 memo to General L.R. Groves - a blueprint for
depleted uranium
Dear Congressman McDermott,
Mr. Joe Pemberton, a lawyer in Bellingham, Washington, has asked me
to provide you with scientific information on the critical and
overlooked issues of particle size, penetration of gas masks, and
mobility of depleted uranium formed under battleground conditions.
It is also powerful scientific information to counter false
statements recently made by the White House and the DOD.
I am writing this letter out of concern for the military personnel
who may now be serving on or near the Gulf War battlefields in
Iraq, and may be quartered in areas already contaminated by
depleted uranium munitions. But they are not my only concern. The
Gulf War Veterans who are now suffering severe health consequences
have also been exposed to depleted uranium, chemicals and
biological materials including vaccines while serving in Iraq and
Kuwait.
The children and people of Iraq have been the greatest victims from
exposure to depleted uranium used in the Gulf War, and will
continue to be. Over time, they cannot escape the chronic, low
level exposure to internal radiation from depleted uranium and its
decay products (see Attach. 7) as it cycles and recycles through
their environment in water, air and food products.
Depleted uranium dust will continue to be an extreme hazard to
soldiers, civilians, populations in countries downwind, and the
environment as a radiological contaminant to all living systems for
ten half-lives or 45 BILLION years.
I am a former Lawrence Berkeley Lab and Lawrence Livermore Lab
scientist, and now work with a group of independent scientists
called the Radiation and Public Health Project. Together this group
has written ten books on the health effects of low-level radiation.
Presently I am writing a science report on depleted uranium for the
United Nations Human Rights Subcommission, now investigating the
illegality and use of depleted uranium munitions. I have written
the Foreword (Attach.1) to 'Discounted Casualties: The Human Cost
of Depleted Uranium' by Akira Tashiro.
Attached (Attach. 2) is a declassified memo to General L. R.
Groves, director of the Manhattan Project, dated October 30, 1943.
Major Doug Rokke provided me with this memo. It summarizes a report
written by Manhattan Project physicists Drs. James B. Conant, A. H.
Compton, and H.C. Urey on the dissemination of very fine
radioactive material as a method of warfare. It is a "blueprint"
for depleted uranium as it has been used in Iraq, Kuwait, Kosovo,
Bosnia and Afghanistan during the past decade. The memo details the
use of very fine and superfine particles of radioactive materials
as a military weapon. Depleted uranium, produces very fine and
superfine particles in large amounts as it burns. The 1943 memo
outlines what was known in 1943, and below are my comments:
-- A gas warfare instrument: the memo indirectly referred to
fission products from Fermi's nuclear pile or radioactive waste
like depleted uranium. The pyrophoric effect of depleted uranium,
which spontaneously burns when heated to 170 C (once it is fired)
and on impact, effectively forms very large numbers of extremely
fine (0.1 micron) and submicroscopic particles as small as 0.001
micron or 10 Ångstroms (see Attach. 3 - Chart
"Characteristics of Particles and Particle Dispersoids") as
described in the memo. Particles in this size range behave like a
gas when inhaled, disperse in the lungs to the blood lung barrier
where the white blood cells (greater than 7microns in diameter)
engulf the tiny particles of depleted uranium and carry them
throughout the body. Once these particles have been engulfed by
blood cells or lodged in tissues, they may not be detectable in the
urine. Contaminated personnel will take the depleted uranium home,
deposited in tissues throughout their bodies.
There is no known treatment for exposure.
- It will permeate a gas mask filter: particles in the 0.1 micron
range will penetrate even a HEPA filter (High Efficiency
Particulate Airfilter - see Attach. 4 - HEPA chart) in large
numbers. The filters in gas masks issued to military personnel are
much less efficient than HEPA filters. There are 1 billion
particles of 0.1 micron diameter in a cubic meter of normal air. It
is clear that a man (without a gas mask) breathing at a normal rate
(about 28 cubic meters per day) and retaining 75% of the very fine
particulate matter in the respiratory system will inhale very large
numbers of very fine particles in a short time period.
In a day, an average man would normally inhale 28 million particles
in the 0.1 micron range through a gas mask with HEPA filters. It
would take one billion fine particles to fill the period at the end
of this sentence. On the battlefield during live fire, the high
concentrations of fine and very fine depleted uranium particles
could increase the numbers inhaled in the small particle range by
magnitudes.
The gas masks issued to military personnel now deployed to the Gulf
Region are defective and do not provide even a minimum of
protection to personnel. Recently I went on a speaking tour in 3
northeastern states with Major Doug Rokke, January 25-February 1,
2003. In nearly every talk we gave, a National Guardsman or other
military person would tell us that their masks fell off when they
tilted their heads.
Air filters in gas masks also fail as they are wetted by moisture
from breathing or are used in the rain.
There is no possible protection from exposure to very fine
particles of depleted uranium through filtering of air.
- As a terrain contaminant: the dispersal of very fine particles of
depleted uranium will contaminate the terrain and deny access to
either side except at the risk of exposure. That includes civilians
and animals who may live there after the battle. The half-life of
depleted uranium - 4.5 billion years - leaves the contaminated
terrain radioactive forever.
Small particles less than 1 micron in diameter do not settle from
the air (see Attach. 3 - Chart "Characteristics of Particles and
Particle Dispersoids") but become incorporated into atmospheric
dust (see Attach. 5 - Chart "Natural Aerosols") and are transported
around the earth until they are removed ("rainout") by rain,
pollution or snow. Seasonal climate change, agricultural
activities, fires and other natural and man-made disturbances will
continue to remobilize particles in the upper dust level
contaminating terrains off the battlefield.
Weathering of larger particles of depleted uranium deposited on the
battlefield will contribute to concentrations of depleted uranium
fine and superfine particles in the air and upper dust level.
Air monitors in Hungary and Greece during bombing in Kosovo and
Bosnia measured Uranium 238 carried by the wind from the
battlefields. Seasonal fluctuations of depleted uranium particles
in the air have been reported in Kuwait.
- Water and food contamination: the depleted uranium dust will
cycle through the environment both on and off the battlefield
contaminating water supplies and food. Food grown in contaminated
areas will be transported to markets and contaminate populations
and areas far from the battlefields. Wind, water, birds and animals
who transport the depleted uranium in their droppings, slowly
contaminate wider and wider areas.
- Internal contamination: inhalation of very fine depleted uranium
dust particles is extremely damaging to the respiratory tract, and
will get into the blood stream where it is carried by blood cells
and contaminates tissues throughout the body. These "hot particles"
will continue to emit alpha and gamma radiation (see Attach. 6 -
photo "Hot particle in lung tissue") as they travel throughout the
body or where they rest in tissue. After the Uranium 238 nucleus
decays, the radioactive daughter product which forms (see Attach.
7) will continue to decay to other isotopes as many as four times.
This will increase the level of radioactive exposure by magnitudes.
Depleted uranium particles lodged in tissue will decay and continue
emitting higher levels of radioactivity from daughter isotopes into
the surrounding tissues.
SYNERGISTIC EFFECTS: The health effects from exposure to a
combination of radiation, chemicals, and biological agents was not
addressed in this WW II memo. This is a critical issue on the
battlefield, and should be considered in studies of Gulf War
Illness. The combination of radiation with heavy metals, chemicals
and biological toxins accelerate and increase the adverse health
effects of exposure. The effects are unknown since very little
research exists in this field.
THIS IS AN ISSUE WHICH SHOULD BE CONSIDERED IN FUTURE CONFLICTS
SUCH AS THE PLANNED BOMBING OF IRAQ.
MEASUREMENTS OF DU IN TISSUES FROM 71 DEAD RESIDENTS OF BASRA:
Dr. Hari Sharma, a radiochemist living in Canada and member of the
Radiation and Public Health Project, has measured depleted uranium
levels in the tissues of 71 residents of Basra who died after the
Gulf War from cancers. They were in the age range of 35-50 years.
He found high concentrations of depleted uranium in tissue samples
from these individuals. The levels were about the same throughout
the tissues, suggesting that very fine particles were transported
in the blood and deposited or lodged throughout the body.
WORLD TRADE CENTER AIR STUDIES:
Dr. Thomas Cahill, Emeritus Professor of Physics and Atmospheric
Sciences at the University of California at Davis, conducted an
independent study of the air around Ground Zero at the World Trade
Center after the 9/11 disaster. Using very sophisticated monitoring
instruments which detect very fine and ultra fine particles, Cahill
and his group monitored the smoldering pile at the WTC for 5 months
following the disaster from one mile north of the center. They
measured concentrations of particles in six size ranges from 2.5
microns to 0.09 microns. They reported the highest concentrations
of very fine particles of metals ever reported in the US, and
unprecedented numbers of very fine and super fine particles. This
air monitoring study of the WTC provided new information about very
fine and superfine particles, which have rarely been studied.
Burning metals and other materials at high temperatures generate
very large amounts of very small particles. For this reason,
depleted uranium which has burned is particularly hazardous.
The EPA has verified that depleted uranium was in the plane that
crashed into the Pentagon on 9/11, and that the crash site was
contaminated. Residents of New York City detected radiation on
hand-held geiger counters at the WTC site. The EPA not only failed
to protect emergency response personnel at both sites, but did not
report or measure concentrations of very fine particles at any of
the 9/11 plane crash locations. These are the most hazardous to
health, and many personnel who worked at the crash sites are now
very ill.
Dr. Cahill also studied the Kuwaiti oil field fires following the
Gulf War.
ECRR: RELEASED JANUARY 30, 2003
A new report from the European Parliament has been released "2003
Recommendations of the European Committee on Radiation Risk: Health
Effects of Ionising Radiation Exposure at Low Doses for Radiation
Protection Purposes" Regulators' Edition: Brussels, 2003. The
report was written by 46 international scientists and has over 550
references to epidemiological studies which include nuclear site
leukemias, Chernobyl infants, minisatellite mutations, weapons
fallout cancers, DU Gulf Veterans, and Iraqi children.
The report concludes that the International Committee on Radiation
Protection (ICRP) determined international standards for risk and
dose effects from studies on A-bomb survivors which were based on
high dose, external, acute exposures. The ICRP model only
considered cancer as a health risk associated with radiation
exposure. The ICRP model, using "bathtub" chemistry, "steam engine"
physics, and deceptive reporting, produced faulty and fraudulent
estimates of risk and dose effects. Additionally, because the ICRP
model is based on acute, high dose, external exposure, it cannot
accurately determine risks or dose response for internal, chronic,
isotopic exposures. For this reason, the ICRP and ECRR models are
mutually exclusive.
This new ECRR report, based on epidemiological studies, concludes
that the health effects of low level radiation exposure have been
underestimated by the ICRP model by 100-1000 times. It also
includes other health effects due to radiation exposure from global
weapons fallout. In addition to cancer, it estimates the number of
foetal deaths and infant mortality, and predicts "a 10% loss of
life quality integrated over all diseases and conditions in those
who were exposed over the period of global weapons fallout".
The committee concluded that underestimates of risk and dose
effects for depleted uranium exposure could be very great since the
effect at the cell level may be very different than other types of
radiation exposures. For this reason, the health effects of
depleted uranium exposure in Gulf Veterans will be investigated in
depth by this committee and will be presented in a new report.
Internal exposure to depleted uranium is a "novel" exposure to an
altered form of natural isotopes. The size, shape, surface texture,
density, chemical composition and other physical and chemical
factors of the particles greatly affect the health impact and
damage to the cells of any biological system from depleted uranium
exposure. Particle size may be the most overlooked and one of the
most important characteristics of depleted uranium dust formed on
the battlefield. After burning, depleted uranium is altered both
physically and chemically and estimates of risk to health and dose
effects cannot be based on previous studies of naturally occurring
uranium. In the Research Report Summaries of depleted uranium
studies done for the military between 1974 and 1999, they clearly
provide information and concerns in these studies about the hazards
of depleted uranium both to health, exposure on the battlefield and
damage to the environment. This summary is well worth reading, as
it provides a timeline of the military politicizing decisions on
the use of depleted uranium over 25 years. For example, in a 1980
Army report:
"This report provides an excellent history of the logic behind the
Army's decision to use DU as a kinetic energy, armored-piercing
munition. DU's final selection over tungsten was based on several
reasons, including the lower initial cost of the penetrator itself
and its better overall performance. DU and tungsten were rated even
for "producibility". Tungsten had the advantage for safety,
environmental concerns, and deployment."
RADIATION RESPECTS NO BORDERS
Depleted uranium is being used as an effective munition on the
battlefield and as a radiological weapon to destroy the genetic
future of the Iraqi people. Before the Gulf War, Iraq was the most
developed and advanced country in the Middle East. Writing,
religion, poetry, music and science began in the region which
includes Iraq, the Cradle of Civilization. The ability of the Iraqi
people has been recognized for millennia. The Iraqi people are more
feared than Saddam Hussein by the US. Their talent for creativity,
ability to be self-determined, and their natural resources have
made them the target of the US Government, US oil companies and the
Department of Defense.
In November of 1991, Richard Berta, the Western Regional Inspector
for the Department of Energy, who was based at the Lawrence
Livermore Lab where I worked, told me: "The Pentagon exists for the
oil companies ..."
The use of depleted uranium by the Department of Defense has
created a slow Chernobyl in the Middle East.
With my best wishes and hopes that this radiation nightmare will
finally come to an end, and with thanks for your efforts to move
the issue into the light,
Leuren Moret
President, Scientists for Indigenous People
City of Berkeley Environmental Commissioner
Past President, Association for Women Geoscientists
2233 Grant Street Apt. 1
Berkeley, CA 94703
Phone/FAX (510) 845-3139
leurenmoret@yahoo.com
REFERENCES:
White House statement on "depleted uranium scare".
http://www.whitehouse.gov/ogc/apparatus/index.html
DOD Colonel Bob Cherry - Letter to Editor, February 2003, Olean
Times Herald.
Letter from Dr. Ernest Sternglass August 23, 2001, RE: "Radiation
and Dust Particles"
Radiation and Public Health Project
http://www.radiation.org
Discounted Casualties: The Human Cost of Depleted Uranium by Akira
Tashiro, Chugoku Shimbun 2001.
http://www.chugoku-np.co.jp/abom/uran/index_e.html
"Estimating the Concentration of Uranium in Some Environmental
Samples in Kuwait After the 1991 Gulf War" by F. Bou-Rabee, Appl.
Radiat. Isol., Vol. 46, No. 4, pp. 217-220, 1995.
Research Report Summaries on Depleted Uranium from 1974-1999,
conducted at National Laboratories and military labs.
http://www.gulflink.osd.mil/du_ii/du_ii_tabl1.htm#TAB%20L_Research%20Report%20Summaries
"Did NATO Attacks in Yugoslavia Cause a Detectable Environmental
Effect in Hungary?" by A. Kerekes et. al, Health Physics, Vol. 80
(2), February 2001, pp.177-178.
"Birds Bring Radioactivity Ashore" by Andy Coghlan, New Scientist,
January 4, 2003, p.5.
2003 Recommendations of the European Committee on Radiation Risk:
Health Effects of Ionising Radiation Exposure at Low Doses for
Radiation Protection Purposes Regulators' Edition: Brussels, 2003.
http://www.euradcom.org
The Petkau Effect - The Devastating Effect of Nuclear Radiation on
Human Health and the Environment by R. Graeub, 2nd Edition, Four
Walls Eight Windows, New York (1994).
Personal communication: email March 28, 2002.
"N.Y. air hazards found: EPA assurances contradicted by UCD
scientists" by E. Lau and C. Bowman, Sacramento Bee February 12,
2002.
SacramentoBee-2-12-02-NYairHazardsFound-EPAassurancesContradictedByUCdavisScientists.pdf
[PDF file] Detection and Evaluation of Long-Range Transport of
Aerosols (DELTA) Group
http://delta.ucdavis.edu/
A Different Nuclear War: Children of the Gulf War by Takashi
Morizumi
http://www.savewarchildren.org
Children of Iraq: The Dream of the Future UNICEF, printed by
Express International - Lebanon (1988).
Richard P. Davitt "A Comparison of the Advantages and Disadvantages
of Depleted Uranium and Tungsten Alloy as Penetrator Materials",
Tank Ammo Section Report No. 107, Dover, NJ: US Army Armament
Research and Development Command, June 1980.
http://www.gulflink.osd.mil/du_ii/du_ii_tabl1.htm#TAB%20L_Research%20Report%20Summaries
"Depleted uranium: devastation at home and abroad" by Leuren
Moret, San Francisco Bay View, November 7, 2001.
http://www.wagingpeace.org/articles/02.01/020117moret.htm
"Tödliches Uran-Recycling" by Geseko von Lüpke, NATUR
January 2002.
http://warp6.dva.de/sixcms/detail.php?id=112520
ATTACHMENTS:
Attachment 1: "Forword" by Leuren Moret to Discounted Casualties:
The Human Cost of Depleted Uranium by Akira Tashiro, Chugoku
Shimbun (2001).
Attachment 2: Declassified memo to General L.R. Groves, Director of
the Manhattan Project, October 30, 1943.
Source - US Army Major Doug Rokke
Attachment 3: TABLE: "Characteristics of Particles and Particle
Dispersoids" from the HANDBOOK OF CHEMISTRY AND PHYSICS 53rd
Edition. This chart provides the particle range which is very wide
for metallurgical dusts and fumes, a range from 100 microns to
0.001 microns (10 Angstroms). Particles smaller than 0.1 microns
will coagulate and form larger particles, but the greatest number
or population of particles will be in the 0.1 micron range (see
Chart "Natural Aerosols"). This particle range is smaller than
blood cells, bacteria, pollens, spores and other typical air
contaminants. Very fine particles are extremely hazardous to health
because they are carried by the blood throughout the body. The rate
of radiation exposure from one very small particle can be more than
is allowed for a whole body exposure in one year (see photo "Hot
particle in lung tissue").
Attachment 4: CHART: "Penetration of a HEPA filter as a function of
particle size" from 18TH DOE NUCLEAR AIRBORNE WASTE MANAGEMENT AND
AIR CLEANING CONFERENCE, Baltimore 1984.
Experimental penetration of particles through a HEPA filter -
determination that approximately 0.1% in the 0.1 micron particle
range will pass through the filter. If there are 100,000 particles
0.1 micron in diameter per cubic centimeter of air, then 120 per
cubic centimeter of air will pass through a HEPA filter. In one day
an average man will inhale 28 million particles in the 0.1 micron
range through a HEPA filter. Attachment 5: CHART: "Natural
Aerosols" from ENCYCLOPEDIA OF SCIENCE & TECHNOLOGY 7th Edition
(1992), McGraw Hill. This chart provides the average size
distribution for natural aerosols in atmospheric dusts. The largest
population or number of particles in an aerosol dust is in the
0.1-0.01 micron range. Depleted uranium particles in this size
range will be incorporated in atmospheric dusts and will travel
indefinitely, transported by winds.
Attachment 6: PHOTO: "Hot" or radioactive particle in lung tissue"
photo by Del Tredici, Burdens of Proof by Tim Connor, Energy
Research Foundation (1997).
This is a photo of a "hot particle", in this case a 1 micron
particle of plutonium, and shows the alpha tracks emitted from that
particle in one year.
Attachment 7: Van Nostrand's Scientific Encyclopedia 5th Edition
(1976)
Decay paths for natural uranium - Table 1 The Uranium Series, and
Table 3 The Actinium Series. The decay paths for uranium are very
complex but decay through a number of steps before they become
stable and are no longer radioactive. Each of these steps produces
a radioactive daughter product which will be more radioactive than
the original uranium atom.
02/21/2005
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