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Depleted
Uranium

Weapons to die for
Depleted Uranium is WMD
The Queen's Death
Star
SILENT WMDs EFFECTS OF
DEPLETED URANIUM
Excellent Resources for
Further Study:

Tehran Times Opinion Column, Aug. 30,
By Leuren
Moret
Weapons to die for
TEHRAN, Aug. 30 (MNA)
-- Two images changed my life when I visited the
Peace Museums in Hiroshima and Nagasaki in August of 2000, on my first trip to
Japan. I had worked as a geoscientist in two U.S. nuclear weapons labs --
Lawrence Berkeley National Lab and Lawrence Livermore National Lab -- but I
never knew what a nuclear weapon really was, nor the horrific effects of
radiation on the environment and biological systems. Now I know.
In the Hiroshima Museum, as a nuclear weapons lab
whistleblower I wandered through the exhibits with TV cameras in my face,
keeping it together by stuffing my emotions. I walked past the mangled lunch
boxes and tricycles, thinking of the school children as I looked at the watches
and clocks stopped at the moment the first thermonuclear weapon detonated on a
human population.
Shadows of people vaporized on stones,
and on the steps of a building where one had sat, waiting for the bank to open
on that fateful morning. A diorama showed the reality of dying people walking
through the streets of Hiroshima with skin dripping and hanging from their
bodies. In another image a man stood looking down at his eyeball he held in his
hand. When I looked up at a model of LITTLE BOY, the atomic bomb dropped on
Hiroshima, I lost it and broke down in sobs which did not stop until half an
hour later, halfway through a press conference. The cameras continued to roll,
capturing my horror and real feelings at the realization that scientists had
made that “gadget” possible. I am a scientist, I worked in those laboratories of
death. And I am a graduate of the University of California, which will forever
be known as “the University that poisoned the world.” The university managed
those laboratories of death, unchallenged, for more than 60 years.
Three days later in the Nagasaki Peace
Museum, I saw FAT MAN, the first plutonium atomic bomb which was dropped on
Nagasaki. There were photos taken by a local photographer just hours after the
bomb destroyed the city. People were standing on a bridge absolutely devastated,
lying on the ground dying, patterns from their kimonos burned into their skin.
And then I saw THE photo: a young mother standing with her kimono open,
barebreasted, with a vacant stare, while she nursed her dying baby. Sobbing
overwhelmed me once again, and it still brings tears to my eyes when I think of
that image, which is burned into my brain by now. I am a mother, and in that
moment I knew that mother could have been me, with the life of my baby taken
from me, or any other mother around the world. Radiation respects no living
thing. That is when I made the decision to spend the rest of my life doing
research and educating the public about radiation. I never knew that I could
make a difference. Now I know that, as a citizen scientist, empowering others is
the best way of all.
I started by writing a Letter to the
Editor, not expecting to have it published, but it was. And then I started
writing articles about depleted uranium which I had learned about from a
journalist, Akira Tashiro, whom I met in Hiroshima on that first trip to Japan.
In 2002 he asked me to write the Foreword to his prize-winning book “Discounted
Casualties: The Human Cost of Depleted Uranium”. Then I was asked to be an
expert witness in Japan for the International Criminal Tribunal for Afghanistan
in 2003. Marion Fulk, a Manhattan Project scientist and Livermore nuclear
weapons program researcher, prepared me with the best science in the world for
my testimony. The testimony resulted in a very strong conviction on depleted
uranium weapons, illegal under all laws, war conventions, U.S. Federal Code, and
U.S. military law. In fact, during testimony, the exposure of the original 1943
Manhattan Project plan to develop DU as a radioactive poison gas weapon
convinced the international panel of Judges to make two additional charges: It
was a crime against the environment, and President George W. Bush was guilty of
war crimes by knowingly exposing his own troops to illegal radioactive weaponry.
My motivation to expose the horrible
truth about depleted uranium resulted in very unexpected successes. One of the
most important actions was taking a bill, introduced and stuck in limbo in the
Connecticut legislature, to New Orleans on a speaking tour in March 2005. I
joined anti-war protestors and veterans marching through the streets of New
Orleans on March 19. We ended up standing on the white marble steps of the
antebellum Louisiana Supreme Court in the heart of the French Quarter. While I
stood in the hot sun describing the horrors of depleted uranium weapons, a
withered grinch of a security guard glared out at me from behind the locked
doors of the Courthouse, while a police van across the street secretly
videotaped our speeches. Bob Smith, a Vietnam veteran, came up afterwards and
asked me for a copy of the Connecticut depleted uranium bill originally written
and introduced by Pat Dillon. Dillon is an epidemiologist and was the Speaker of
the House in Connecticut, a position she lost shortly after her bill was
introduced.
Much to my complete shock, Bob Smith and
Ward Reilly, two Vietnam era veterans, took it to the Louisiana legislature.
They told two legislators willing to introduce the bill to “white out
Connecticut and write in Louisiana.” It was quickly passed unanimously by the
legislature and signed into law by the governor within a few months. What I
didn’t know then was that the bill would set states rights against federal
rights, and National Guardsmen against regular military personnel, busting the
depleted uranium issue open on a national scale. Because state governments have
legal jurisdiction over the National Guard, the state bill requiring mandatory
testing for depleted uranium exposure did not cover regular military personnel.
This angered the regular soldiers who were frustrated and angry over being
“kicked to the curb” by the Pentagon and Veterans Administration. The state is
legally entitled to force the Pentagon to pay the costs of implementing the
bill, because the Pentagon is in violation of its own mandates, directives and
orders, which require training, testing and treatment for soldiers handling
depleted uranium.
In May of 2005, Congressman Jim
McDermott, M.D. (D-WA), introduced a depleted uranium bill in Congress. Attached
to the bill as a supporting document was an entire issue of President Bush’s
hometown newspaper in Crawford, Texas, The Lone Star Iconoclast, which Leon
Smith, the editor, had dedicated to “What is DU?.” On March 1, 2006, a second
issue, “Have DU Will Travel,” came out with extensive interviews with
scientists. After covering Cindy Sheehan and Camp Casey last summer, the paper
is now widely read in Washington, D.C. Recently, Leon Smith published a book
called “The Vigil: 26 Days in Crawford, Texas” about Camp Casey.
Today, more than 15 states have
introduced a depleted uranium bill, and Louisiana and Connecticut have passed
theirs. It has created a nightmare for the federal government and put the
Pentagon in permanent PR counterspin as well as exposed 15 years of official
coverup under three Presidents and corruption in Congress. Our children, our
sons and daughters, have been sent off to the battlefields of the Middle East
and Central Asia to become uranium meat. The cost of their care has been dumped
on the state medical facilities. Their families have been destroyed, not to
mention their lives. It is time for citizens and state elected officials to pass
depleted uranium bills which will help all soldiers by putting pressure on the
federal government.
Each of us has a part to play by
demonstrating at local facilities like Alliant (manufacturer of depleted uranium
weapons), writing letters to local newspapers, contacting elected officials,
counter-recruiting in schools, or just passing on the information so that others
can become aware. Put a song in their hearts by sending “Johnny Got A Gun” to
your local radio station or Indymedia site to play on the air. Depleted uranium
is Washington’s secret nuclear war.
Leuren Moret is an independent scientist
and environmental commissioner in the City of Berkeley. She is featured in
documentary films on depleted uranium: BEYOND TREASON (2005), BLOWIN’ IN THE
WIND (2005), BAGDAD RAP (2004). They can be purchased by contacting her at
leurenmoret@yahoo.com. She also does speaking events.
(PulseTC.com)
Publish date,Tehran: 2006/08/30, 20:51 © 2003-2005 Mehr
News Agency
Published on Tuesday, August 9, 2005 by the
Battle Creek Enquirer (Michigan)
Depleted Uranium is WMD
by Leuren Moret
My grandfather, U.S. Army Col. Edwin Joseph McAllister, was born in Battle
Creek in 1895. He does not know that his first grandchild is an international
expert on depleted uranium. I have worked in two U.S. nuclear weapons
laboratories, and in 1991 I became a whistleblower at the Livermore lab.
Depleted uranium is very, very, very nasty stuff:
Depleted uranium (DU) weaponry meets the definition of weapon of mass
destruction in two out of three categories under U.S. Federal Code Title 50
Chapter 40 Section 2302.
DU weaponry violates all international treaties and agreements, Hague and
Geneva war conventions, the 1925 Geneva gas protocol, U.S. laws and U.S.
military law.
Since 1991, the U.S. has released the radioactive atomicity equivalent of at
least 400,000 Nagasaki bombs into the global atmosphere. That is 10 times the
amount released during atmospheric testing which was the equivalent of 40,000
Hiroshima bombs. The U.S. has permanently contaminated the global atmosphere
with radioactive pollution having a half-life of 2.5 billion years.
The U.S. has illegally conducted four nuclear wars in Yugoslavia,
Afghanistan and twice in Iraq since 1991, calling DU "conventional" weapons when
in fact they are nuclear weapons.
DU on the battlefield has three effects on living systems: it is a heavy
metal "chemical" poison, a "radioactive" poison and has a "particulate" effect
due to the very tiny size of the particles that are 0.1 microns and smaller.
The blueprint for DU weaponry is a 1943 Manhattan Project memo to Gen. L.
Groves that recommended development of radioactive materials as poison gas
weapons - dirty bombs, dirty missiles and dirty bullets.
DU weapons are very effective kinetic energy penetrators, but even more
effective bioweapons since uranium has a strong chemical affinity for phosphate
structures concentrated in DNA.
DU is the Trojan Horse of nuclear war - it keeps giving and keeps killing.
There is no way to clean it up, and no way to turn it off because it continues
to decay into other radioactive isotopes in over 20 steps.
Terry Jemison at the U.S. Department of Veterans Affairs stated in August
2004 that over 518,000 Gulf-era veterans (14-year period) are now on medical
disability, and that 7,039 were wounded on the battlefield in that same period.
Over 500,000 U.S. veterans are homeless.
In some studies of soldiers who had normal babies before the war, 67 percent
of the post-war babies are born with severe birth defects - missing brains,
eyes, organs, legs and arms, and blood diseases.
In southern Iraq, scientists are reporting five times higher levels of gamma
radiation in the air, which increases the radioactive body burden daily of
inhabitants. In fact, Iraq, Yugoslavia and Afghanistan are uninhabitable.
Cancer starts with one alpha particle under the right conditions. One gram
of DU is the size of a period in this sentence and releases 12,000 alpha
particles per second.
Before my grandfather died, he told me that his generation had made a mess of
this planet. I wonder what he would say to me now I would tell him to see
"Beyond Treason" (www.beyondtreason.com),
a new documentary about the history of treason by the U.S. government against
our own troops: Atomic veterans, MK-Ultra, Agent Orange and DU. After Vietnam,
Henry Kissinger said, "Military men are just dumb, stupid animals to be used as
pawns in foreign policy. . ." (from Chapter 5 in the "Final Days" by Woodward
and Bernstein).
Leuren Moret is an international radiation specialist, with a B.S.
degree in geology from University of California at Davis, a M.A. degree in Near
Eastern studies from University of California at Berkeley and has done
post-graduate work in the geosciences at UC-Davis. She is environmental
commissioner for the City of Berkeley, Calif.
© 2005 Battle Creek Enquirer
The Queen's Death
Star
Depleted Uranium
Measured in British Atmosphere from
Battlefields in the Middle East
LEUREN MORET / Mindfully.org
26feb2006
[More by
Leuren Moret]
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Leuren Moret
President, Scientists for Indigenous People
City of Berkeley Environmental Commissioner
Past President, Association for Women Geoscientists
Berkeley, CA
Phone/FAX (510) 845-3139
leurenmoret@yahoo.com
[More by
Leuren Moret] |
"Did the use of Uranium weapons in Gulf War II result in contamination of
Europe? Evidence from the measurements of the Atomic Weapons Establishment
(AWE), Aldermaston, Berkshire, UK," reported the Sunday Times Online (February
19, 2006) in a shocking
scientific study authored by British scientists Dr. Chris Busby and
Saoirse Morgan.
The highest levels of depleted uranium ever measured in the atmosphere in
Britain, were transported on air currents from the Middle East and Central Asia;
of special significance were those from the Tora Bora bombing in Afghanistan in
2001, and the "Shock & Awe" bombing during Gulf War II in Iraq in 2003.
Out of concern for the public, the official British government air monitoring
facility, known as the Atomic Weapons Establishment (AWE), at Aldermaston, was
established years ago to measure radioactive emissions from British nuclear
power plants and atomic weapons facilities.
The British government facility (AWE) was taken over 3 years ago by
Halliburton, which refused at first to release air monitoring data to Dr. Busby,
as required by law.
An international expert on low level radiation, Busby serves as an official
advisor on several British government committees, and co-authored an independent
report on low level radiation with 45 scientists, the European Committee on
Radiation Risk (ECRR), for the European Parliament. He was able to get
Aldermaston air monitoring data from Halliburton /AWE by filing a Freedom of
Information request using a new British law which became effective January 1,
2005; but the data for 2003 was missing. He obtained the 2003 data from the
Defence Procurement Agency.
The fact that the air monitoring data was circulated by Halliburton/ AWE to
the Defence Procurement Agency, implies that it was considered to be relevant,
and that Dr. Busby was stonewalled because Halliburton/ AWE clearly recognized
that it was a serious enough matter to justify a government interpretation of
the results, and official decisions had to be made about what the data would
show and its political implications for the military.
In a similar circumstance, in 1992, Major Doug Rokke, the Director of the
U.S. Army Depleted Uranium Cleanup Project after Gulf War I, was ordered by a
U.S. Army General officer to write a no-bid contract "Depleted Uranium,
Contaminated Equipment, and Facilities Recovery Plan Outline" for the procedures
for cleaning up Kuwait, including depleted uranium, for Kellogg, Brown and Root
(KBR), a subsidiary of Halliburton.
The contract/proposal was passed through Madeleine Albright, the Secretary of
State, to the Emirate of Kuwait, who considered the terms and then hired KBR for
the cleanup.
Aldermaston is one of many nuclear facilities throughout Europe that
regularly monitor atmospheric radiation levels, transported by atmospheric sand
and dust storms, or air currents, from radiation sources in North Africa, the
Middle East and Central Asia.
After the "Shock and Awe" campaign in Iraq in 2003, very fine particles of
depleted uranium were captured with larger sand and dust particles in filters in
Britain.
These particles traveled in 7-9 days from Iraqi battlefields as far as 2400
miles away.
The radiation measured in the atmosphere quadrupled within a few weeks after
the beginning of the 2003 campaign, and at one of the 5 monitoring locations,
the levels twice required an official alert to the British Environment Agency.
In addition to depleted uranium data gathered in previous studies on Kosovo
and Bosnia by Dr. Busby, the Aldermaston air monitoring data provided a
continuous record of depleted uranium levels in Britain from the other recent
wars.
Extensive video news footage of the 2003 Iraq war, including Fallujah in
2004, provided irrefutable documented evidence that the US has unethically and
illegally used depleted uranium munitions on cities and other civilian
populations.
These military actions are in direct violation of not only the international
conventions, but also violate US military law because the US is a signatory to
The Hague and Geneva Conventions and the 1925 Geneva Gas Protocol.
TITLE 50 > CHAPTER 40 > § 2302
§ 2302. Definitions
Release date: 2005-03-17
In this chapter:
(1) The term “weapon of mass destruction” means any weapon
or device that is intended, or has the capability, to
cause death or serious bodily injury to a significant
number of people through the release, dissemination,
or impact of—
(A) toxic or poisonous chemicals or their precursors;
(B) a disease organism; or
(C) radiation or radioactivity.
(2) The term “independent states of the former Soviet Union”
has the meaning given that term in section 5801 of
title 22.
(3) The term “highly enriched uranium” means uranium
enriched to 20 percent or more in the isotope U–235.
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Depleted uranium weaponry meets the definition of a Weapon of Mass
Destruction (WMD) in two out of three categories under US Code TITLE 50,
CHAPTER 40 Sec. 2302 [at right].
After action mandates have also been violated such as US Army Regulation AR
700-48 and TB 9-1300-278 which requires treatment of radiation poisoning for all
casualties, including enemy soldiers and civilians, and remediation.
Dr. Busby's request for this data through Halliburton from AWE, and
subsequently provided by the Defence Procurement Agency, was necessary to
establish verification of Iraq's 2003 depleted uranium levels in the atmosphere.
These facts demonstrate why Halliburton (AWE) refused to release the 2003
data to him, and it obviously establishes that weaponized depleted uranium is an
indiscriminate weapon being distributed all over the world in a very short
period of time, immediately after its use.
The recent documentary film
BEYOND
TREASON details the horrific effects of depleted uranium exposure on
American troops and Iraqi civilians in the Gulf region in 1991; not to speak of
those civilians continuing to live in permanently contaminated and thus
uninhabitable regions.
Global increases since 1991 of melanoma, infant mortality, and frog die-offs
can only be explained by an environmental contaminant. Alarming global increases
in diabetes, with high correlation to depleted uranium wars in Iraq,
Bosnia/Kosovo, and Afghanistan, demonstrate that diabetes is a sensitive
indicator and a rapid response to internal depleted uranium exposure.
Americans in 2003 reported visiting Iraqi relatives in Baghdad who were
suffering from an epidemic of diabetes.
After returning to the US following 2-3 weeks in Iraq, they discovered within
a few months that they too had diabetes.
Japanese human shields and journalists who worked in Iraq during the 2003 war
are sick and now have symptoms typical of depleted uranium exposure.
Likewise, after the US Navy, several years ago, moved depleted uranium
bombing and gunnery ranges from Vieques Island in Puerto Rico to Australia,
health effects there are already being reported.
The documentary film
BLOWIN' IN THE WIND, has an interview with a family with two normal
teenage daughters, living near the bombing range where depleted uranium weaponry
is now being used.
The parents showed photos of their baby born recently with severe birth
defects. The baby looked like Iraqi deformed babies, and like many of the Iraqi
babies, died 5 days after birth.
Other than anonymous British government officials denying that Iraq was the
source of the depleted uranium measured at Aldermaston by AWE, and some unnamed
'establishment scientists' blaming it on local sources or natural uranium in the
Iraq environment, there is no one, as of this writing, willing to lend their
name or office to refuting this damning evidence reported by Dr. Busby.
All of the anonymous statements used by the media thus far are contradicted
by the factual evidence found in the filters, which was all transported from the
same region.
The natural abundance of uranium in the crust of the earth is 2.4 parts per
million, which would not become concentrated to the high levels measured in
Britain during a long journey from the Middle East. These particles traveling
over thousands of miles would dilute the concentration rather than increase it.
There are no known natural uranium deposits in Iraq which make it impossible
for these anonymous claims to have scientific credibility.
Unnamed government sources blamed local sources in Britain such as nuclear
power plants; however that would also leave evidence of fission products in the
filters which were not in evidence.
The lowest levels measured at monitoring stations around Aldermaston were at
the facility, which means it could not be a possible source. Atomic weapons
facilities would be more likely to produce plutonium contamination, also not
reported as a co-contaminant at Aldermaston.
In other words, all factual evidence considered, the question must be asked,
what were the media's anonymous experts and government officials basing their
claims on?
Dr. Keith Baverstock exposed a World Health Organization (WHO) cover-up on
depleted uranium in an Aljazeera article, "Washington's Secret Nuclear War"
posted on September 14, 2004. It was the most popular article ever posted on the
Aljazeera English language website.
Baverstock leaked an official WHO report that he wrote, to the media several
years ago after the WHO refused to publish it. He warned in the report about the
mobility of, and environmental contamination from, tiny depleted uranium
particles formed from US munitions.
Busby's ECRR report challenged the International Committee on Radiation
Protection (ICRP) standards for radiation risk, and reported that the mutagenic
effects of radiation determined by Chernobyl studies are actually 1000 times
higher than the ICRP risk model predicts.
The ECRR report also establishes that the ICRP risk model, based on external
exposure of Hiroshima and Nagasaki victims, and the ECRR risk model, based on
internal exposure, are mutually exclusive models. In other words, the ICRP risk
model based on external exposure cannot be used to estimate internal exposure
risk.
The report also states that a separate study is needed for depleted uranium
exposure risks, because it may be far more toxic than nuclear weapons or nuclear
power plant exposures. In July of 2005, the National Academy of Sciences
reported in their new BEIR VII report on low level radiation, that there is "no
safe level of exposure".
The report also finally admitted that very low levels are more harmful per
unit of radiation than higher levels of exposure, also known as the "supralinear"
effect.
This is extremely alarming information on low level radiation risk, since the
AWE data from Aldermaston confirms that rapid global transport of depleted
uranium dust is occurring.
Dr. Katsuma Yagasaki, a Japanese physicist at the University of the Ryukyus
in Okinawa, has estimated that the atomicity equivalent of at least 400,000
Nagasaki bombs has been released into the global atmosphere since 1991, from the
use of depleted uranium munitions.
It is completely mixed in the atmosphere in one year. The "smog of war" from
Gulf War I was found in glaciers and ice sheets globally a year later.
Even more alarming is the non-specific catalytic or enzyme effect from
internal exposures to nanoparticles of depleted uranium. Soldiers on depleted
uranium battlefields have reported that, after noticing a metallic taste in
their mouths, within 24-48 hours of exposure they became sick with Gulf War
syndrome symptoms.
Who is profiting from this global uranium nightmare? Dr. Jay Gould revealed
in his book THE ENEMY WITHIN [see
excerpt], that the British Royal family privately owns investments in
uranium holdings worth over $6 billion through Rio Tinto Mines.
The mining company was formed for the British Royal family in the late 1950's
by Roland Walter "Tiny" Rowland, the Queen's buccaneer.
Born in 1917 through illegitimate German parentage, and before changing his
name, Roland Walter Fuhrhop was a passionate member of the Nazi youth movement
by 1933, and a classmate described him as "...an ardent supporter of Hitler and
an arrogant, nasty piece of work to boot."
His meteoric rise and protection by intel agencies and the British Crown are
an indication of what an asset he has been for decades to the Queen, as Africa's
most powerful Western businessman.
Africa and Australia are two of the main sources of uranium in the world. The
Rothschilds control uranium supplies and prices globally, and one serves as the
Queen's business manager.
Filmmaker David Bradbury made BLOWIN' IN THE WIND to expose depleted uranium
bombing and gunnery range activities contaminating pristine areas of eastern
Australia, and to expose plans to extract over $36 billion in uranium from mines
in the interior over the next 6 years. Halliburton has finished construction of
a 1000 mile railway from the mining area to a port on the north coast of
Australia to transport the ore.
The Queen's favorite American buccaneers, Cheney, Halliburton, and the Bush
family, are tied to her through uranium mining and the shared use of illegal
depleted uranium munitions in the Middle East, Central Asia and Kosovo/Bosnia.
The major roles that such diverse individuals and groups as the Carlyle
Group, George Herbert Walker Bush, former Carlyle CEO Frank Calucci, the
University of California managed nuclear weapons labs at Los Alamos and
Livermore, and US and international pension fund investments have played in
proliferating depleted uranium weapons is not well known or in most instances
even recognized, inside or outside the country.
God Save The Queen from the guilt of her complicity in turning Planet Earth
into a "Death Star."
[See:
Did the use of Uranium weapons in Gulf War 2 result in contamination of Europe?
Busby & Saoirse1jan06]
Global Diabetes Epidemic Caused By Depleted Uranium From Leuren Moret 8-23-6
Here are two maps of Lebanon indicating the amount of munitions used on
targets, and what parts of the infrastructure were destroyed in Lebanon, by
Israeli military attacks. These are from an Italian journalist, Liliana Bourgana,
who sent them to me - the maps are official Lebanese govt. data.
Map 1 
Map 2 
You can go to the Lebanese govt. website listed on the maps for updates. The
journalist will be interviewing me on Aug. 28 regarding the weapons that were
used. This information is from my own observations in news coverage I saw on
Italian TV and the BBC while I was in Italy July 4-July 18, and from Major Doug
Rokke who was in charge of the Depleted Uranium cleanup team in the Gulf after
GW I:
* cluster bombs
* depleted uranium bombs - including an order during the war by Israel from
the US for 100 more GBU-28 5000 lb. depleted uranium warhead bombs [I was in
Italy July 4-27 and saw depleted uranium bombs on Italian news and the BBC.
Israeli military planes bombed Beirut, the airport and southern Lebanon with DU]
* depleted uranium 105mm and 120mm tank rounds [Info from Major Doug Rokke
which he saw in the news]
* missiles (probably DU)
* white phosphorous weapons
* Baccilus globigii - bioweapon which makes people throw up violently but
does not kill. (A military source said this was determined from color coding on
the weapons) This was used in southern Lebanon and reported that it suddenly
caused people to get sick.
* Reports from MDs treating the wounded describing new kinds of wounds never
seen before which may be laser weapons. The US has them (classified) on the
ABRAMS tanks. There were certainly Directed Energy Weapons
(DEW) used by Israel because shrunken bodies and other types of indicators
were reported by Lebanese MDs, descriptions exactly like wounds etc. reported in
Baghdad at the airport in 2003 and since.
- Toxic chemicals
Lebanese MDs working with the dead and wounded reported horrific new types of
wounds and causes of death. In every war new weapons are tested and old weapons
are dumped.
I will continue to do interviews regarding the illegal use of depleted
uranium weaponry, a radioactive poison gas weapon, which has now polluted the
entire global atmosphere and has been measured in the British atmosphere within
7-9 days of its use on the battlefields of Iraq, Yugoslavia, and Afghanistan:
'THE QUEEN'S DEATH STAR' By Leuren Moret http://www.mindfully.org/Nucs/2006/DU-Europe-Moret26feb06.htm
'Depleted Uranium is WMD' By Leuren Moret http://www.commondreams.org/views05/0809-33.htm
Yes it travels... very rapidly at relatively low altitude in the troposphere,
and is carried by westerlies, trade winds, convection cells, and air currents,
not to mention the sand and dust storms which are characteristic of arid
regions. It is traveling west across the Atlantic on the westerlies at about
10,000 feet, north into Europe, and east where it is blowing off the Himalayas
and contaminating northern India.
We are now in a global diabetes epidemic since 1991 as a result of global
contamination from depleted uranium. India now has 39 million diabetics and
expects 50 million by 2010 (in third world countries 80% is undiagnosed). The US
Centers for Disease Control reported in 1980 that there were 5.7 million
diagnosed cases of diabetes. That number increased by 1 million in a decade, in
1990, to 6.7 million.
Between 1990 and 2002 the number increased to 13.5 million, with the largest
increase of 2 million in a single year between 1996-97. That was the year
Clinton did heavy grid and carpet bombing... now we know it was with massive
amounts of depleted uranium dirty bombs. This huge increase in diabetes is
consistent with Japanese public health increases in diabetes and cancer
mortality as well as other radiation related illnesses, also increases in India,
and the UK.
This planet is enveloped in depleted uranium radioactive poison dust, and
with all the other problems, it is causing the greatest mass extinction in 65
million years since the dinosaurs went extinct. 50% of the worlds species will
be extinct within 100 years. Infertility in humans is an increasing problem now,
with only 15% of sperm in men globally which is normal. It used to be 80% was
normal.
Britain and the US... and now Israel... have turned this planet into the
Auschwitz radioactive poison gas chamber and we are all sitting in it increasing
our body burden of radiation with every breath we take. There is no escape...
I received an email "Thank god Bush finally nuked Israel... all we have to do
is sit and wait now." As bad as this sounds, the reality is that it is not a
joke. Israel has been contaminated from French atmospheric testing in the
Sahara, Dimona (their own nuke program), depleted uranium used in
Iraq/Yugoslavia/Afghanistan and now... Lebanon. This will contaminate the entire
Mediterranean, Europe, and beyond... wherever the winds take it, to be rained
and snowed out in our back yards.
Thanks
Leuren Moret
leurenmoret@yahoo.com
SILENT WMDs EFFECTS OF DEPLETED URANIUM
By Admiral Vishnu Bhagwat
Former Chief of the Naval Staff, India
FEBRUARY 29, 2004
Heat not a furnace for your foe
so hot ..that it do singe yourself.
-
William Shakespeare
This brief presentation is aimed
at conveying to the primarily Indian participants of the Conference the fateful
and disastrous consequences of the indiscriminate use of depleted and non DU
munitions on the people of the west, central and south Asian regions, women,
children , men , animals, plant and animal life now and in the future, in gross
violation of international law, the Hague convention and domestic US military
law.
Official Gamma Ray damage caused
studies have been deficient in a number of respects..internal contamination,
internal dose to individual cells, omissions of diseases other than cancer,
mutagenic, long term degeneration , oncogenesis, effects of the killer isotopes
in particular. The case studies of the years 1945-50 were ignored. A recent
European Parliament Report ECRR 2003 (European Committee on
Radiation Risk ) concludes that A Bomb studies underestimate the radiation
risk by more than 1000 times and failed to consider the internal exposure and
diseases caused by Alpha and Beta rays. They did not consider the
Manhattan Project classified memo that, in case the Project objective of
producing Plutonium fission and theA Bomb did not succeed , Depleted Uranium
munitions would be deployed towards the attainment of the same objective (encl.
1).
DU weapons emit Alpha particle
dose to a single cell from U-238 which is 50 times the annual dose level. Cancer
is initiated with one alpha particle, its daughter isotopes effect generations
as the isotopes bio-concentrate in plants and animals, and travel up the food
chain. It is a nuclear weapon because the energy is derived from the nucleus of
the atom. They enter the body through the lungs, the digestive system or breaks
in the skin. One gram of DU releases more than 12,000 particles per second. The
radiation slowly kills the cells that make life possible. The Gulf War syndrome
of 1991 did just that ( reported by Dr Asaf Durakovic, Prof. of Medicine ,
Georgetown University, and discoverer of the Gulf War Syndrome.)
We are well aware that the
radiation fall-out map Under the Cloud: Decades of Nuclear Testing has
demonstrated the effects of 1200 nuclear weapon tests conducted at the Nevada
Test Site; and the US Government admitted in Nov. 2002, that every living person
in the US between 1958-63 was exposed to this fall out resulting in cancer,
gene mutation, heart disease, autism, diabetes, Parkinsons, ALS, asthma, chronic
fatigue syndrome , hypothyroidism in new-borns, obesity and learning
disabilities. One out of twelve children in the US is disabled. The fall out
did not stop at the US borders. It travelled around the world, as atmospheric
dust and remains even in the biosphere/ sub-orbital space today. High breast
cancer rates have been co-located in the proximity of nuclear power plants in
the west and more so in the east coast areas of the US (The Breast cancer map
from The Enemy Within: the high cost of living near nuclear reactors, quotes
US Govt. Disease Control Centers.
The Radiation & Public health
Report (RPHP), rendered by a group of independent scientists collected 4000 baby
teeth and by measuring Strontium 90 levels in the baby teeth ( a built in dosi-meter
) they have been able to co-relate with radiation related diseases in children
living near the nuclear power plants; the main path ways being dairy products
and drinking water.
The induction of DU weapons in
1991 in Iraq, the radio-active trash from nuclear plants broke a 46 year taboo.
This Trojan Horse of nuclear war, an omnicidal weapon has since then continued
to be used more and more. DU remains radioactive longer than the age of the
earth ( estimated at 4.5 billion years. )
The long-term effects from over a
decade of DU exposures are emerging in Southern Iraq. They are devastating. The
increased quantities of radio-active material ( including non-depleted
uranium), used in Afghanistan are 3 to 5 times greater than Iraq 199. In Iraq
2003 they are already estimated to be 6 to 10 times 1991 and will travel through
a larger area and affect many more people, babies and unborn. Countries within
a 1000 mile radius of Baghdad and Kabul are being affected by radiation
poisoning , that includes the Capital, New
Delhi, where the ruling elite lives. The reported coming of an AIDS epidemic
last year in India , down wind, may have a relationship to DU bombing in
Afghanistan. If we think cancer is a problem now wait until more DU is released
in wars against terror and for regime change, on mistaken Intelligence
reports.
More than 500 tons of DU
munitions have been dispensed in Afghanistan. Professor Yagasaki calculated
that 800 tons of DU is the atomicity equivalent to 83,000 Nagasaki bombs in a
paper presented at the World Uranium Weapons Conference in Hamburg in October
2003 ( 5 months ago ). The amount of DU used in Iraq in 2003 is equivalent to
nearly 250,000 Nagasaki bombs ( Busby and Leuren Moret have calculated that
1900 tons of DU is equivalent to 60 TBq of Alfa and Beta particulate activity).
We need not ennumerate the DU
munition types used in Iraq 199, Kosovo 1999, Afghanistan 2001-04 and Iraq
2003. They have been dispensed by all air / ground and sea systems on innocent
civilians. DU burns intensely and is very hard. It releases Uranium Oxide.
The aerosol contains particles of 0.5-5 microns in size, once they are in the
air or dust they are inhaled or ingested, including from contaminated soil.
Once in the lungs one such particle is equivalent to having one XRay per hour,
for life. Because it is impossible to remove, the victim is gradually
irradiated. Still births, birth defects, leukemia, damaged central nervous
systems and other cancers have been common in children born since 1991. Child
leukemia has risen 600 % in areas of Iraq as reported by the Netherland Visie
Foundation. Beyond just the health
consequences, DU munitions are in fact, weapons of Silent Mass Destruction in
so far as the consequences of their usage are vast, indiscriminate and violate
all Human Rights Conventions . Tora Bora , Kabu , Paktia , Karises or underwater
supply tunnels have been contaminated forever. All this has been documented in a
comprehensive paper Uranium wars : The Pentagon steps up its use of
Radio-active Munitions, by Marc W. Herold to whom this paper owes sincere
acknowledgement.
In another paper Dr Mohammed Daud
Miraki, Director Afghan DU Recovery Fund, quotes George W Bush , we will smoke
them out, condemning the unborn, the living and the future generations of
Afghans and the neighbouring people to a pre-determined, death sentence. After
the destruction of our village, I realised that the Americans had sentenced us
all to death. When I saw my deformed
grandson I realised my hopes for the future have vanished This time we are
part of the invisible genocide brought on by America a silent death from which
we will not escape ( Jooma Khan of Laghman province..March 2003.) Similar
stories are repeated from Paktita province of Jelly Babies. Pregnant women
are afraid of giving birthThis is the legacy of US ushered liberation, freedom
and democracy. DU is cheap for the US, utilising nuclear waste, cheaper than
titanium and tungsten, not for the liberated (non-DU is still cheaper as it is
the uranium feedstock, pre-enrichment).
The Uranium Medical Research
Center (UMRC), Washington DC, and the Bulletin of Atomic Scientists (1991) -
Steve Fetter and Frank Von Hippel have reported on extensive research by Field
teams of the UMRC in Afghanistan. Testimonies of fathers and mothers are
horrifying What else do the Americans want ? They killed us , they turned our
new-borns into horrific deformations, and they turned our farm lands into
grave-yards, and destroyed our homes. On top of all this their planes fly over
and spray us with bullets.. we have nothing to lose ..we
will fight them the same way we fought the previous invaders (Sayed Gharib at
Tora Bora).
Radiological dispensing devices
or warfare is the latest of the weapons of the new millenium, but it singes even
those who use it , as shown in the after effects of the tests at home ground in
the US, where evidence of cognitive damage during early infancy have been
compiled. For us in Eurasia, Pakistan and India we have a new health epidemic
to drain our scarce resources.
As world citizens we need to
focus on a new scourge, the reality of the PNAC - Rebuilding Americas
Defenses, Strategy, Forces and Resources for a New Century.
The Report notes that , Much
has been written in recent years about the need to transform the conventional
armed forces of the United States to take advantage of the Revolution in
Military Affairs. Our military requires a dramatic transformation , lest we
lose our ability to fight the future unconventional wars .. some may be fought
in cyberspace, others under water or in outer space . And some even within our
bodies.
Paul Wolfowitz, William Kristol
and others are some of the men representing contemporary power centers, who
define US policy. History indicates that the men who define US military policy
from the shadows , are worthy of our attention.
GENETIC BOMBS
When creating genetic-bombs
or weapons to target specific groups; genetic profiles are subtler and more
accurate than the coarse pseudo category called race. The group with ADHD ( the
Edison Gene) uniquely share common inherited variations in their dopamine
regulating genes regardless of race, geography or ethnicity. Thus anybody
whos part of a group with a shared genetic profile may be at risk in the
future.
A virus or bacteria may attack
only a particular type of person, killing, disabling or sterilising only those
of a particular gene profile.
Threatening a particular type would be sufficient political black-mail.
Wolfowitz, Kristol and their
colleagues suggested that the Pentagon should be thinking about not just germ
warfare of which they have plenty of capabilities, but gene warfare.
Genetic terra-forming could
replace diplomacy, or it could change the face of politics if an organism got
loose that killed all the people of a particular minority community who tend to
vote for a particular political party.
According to the PNAC,
Genetically targeted weapons could change world politics for ever, and the
report notes, advanced forms of biological warfare that can target specific geno-types
may transform biological warfare from the realm of terror to a politically
useful tool
To conclude 4th generation
micro-nukes, with their war-head composition, were deliberated upon and decided
at the US Airforce Strategic Command Headquarters at the Offutt Airforce Base,
Nebraska, between the top Corporates /weapon manufacturers and the US military
brass. The former not only have prior knowledge of numbers and types of all
types of nuclear weapons, but the locations of the planned and approved targets,
globally.
This meeting took place on
Hiroshima Day, 6th August, 2003, and to reiterate, the aim was to define a new
generation of nuclear weapons to be used on a pre-emptive basis against rogue
enemies and terrorist organisations. (mini-nukes have an explosive capacity
between one-third and six times a Hiroshima bomb).
In this Strangelovian logic,
nuclear weapons are now viewed as a means to ensuring peace and security against
non-existent WMDs.
AT A GLANCE:
1. In the 2003 war, the IraqiS were
subjected to the Pentagons radioactive arsenal, mainly in the urban centers,
unlike in the deserts in 1991. The aggregate effects of illnesses and long term
disabilities and genetic birth defects will be apparent only 2008 onwards.
2. By now, half of all the 697,000 US soldiers involved
in the 1991 war have reported serious illnesses. According the American Gulf
War Veterans Association, more than 30% of these soldiers are chronically ill,
and receiving disability benefits from the Veterans Administration.
3. The number of disabled veterans is shockingly high . They are in their
mid-thirties and should have been in the prime of health.
4. Near the Republican Palace where US troops stood guard and over 1000
employees walked in and out, the radiation readings were the hottest in Iraq,
at nearly 1900 times background radiation levels.
5. At a roadside stand, selling fresh bunches of parsley, mint, and onions,
children played on a burnt out Iraqi tank just outside Baghdad, the Geiger
counter registered 1000 times normal background radiation.
6. The Pentagon and the United Nations estimate that the US and Britain used
1,100 to 2,200 tons of armor piercing shells made of DU during attacks in
March-April 2003, far more than the 1991 Gulf War (this does not include air
dispensed DU munitions and missiles), wrote the Post Intelligencer.
7. An otherwise useless by-product of the uranium enrichment process, DU is
attractive to military contractors because it is so cheap and often offered for
free by the Government.
8. The long term effects, as Dr Asaf Durakovic elaborates, after the early
neurological symptoms are cancer, and related radiation illnesses such as
chronic fatigue syndrome, joint and muscle pain, neurological and/or nerve
damage, mood disturbances, auto-immuno deficiciencies, lung and kidney damage,
vision problems, skin rupture, increase in miscarriages, maternal mortality and
genetic birth defects/deformation.
9. For years the US government described the Gulf War Syndrome as a post
traumatic stress disorder. It was labelled as a psychological problem or simply
as mysterious unrelated ailments much in the same way as health problems of
Vietnam veterans suffering from Agent Orange poisoning.
( With acknowledgements to Sara Flounders, for 1-9 above, Coordinator
of the DU education program ).
I also gratefully acknowledge the facts learnt from evidence
led by scientists/papers presented and accepted by the International Criminal
Tribunal on Afghanistan, at Tokyo on 13-16 Decembe, 2003 and earlier at the
World Depleted Uranium Weapons Conference, Hamburg 16-19 October, 2003, by
Leuren Moret, whose continuing contribution to this cause against Silent
Wepons of Mass Destruction (SWMD), in defense of humanity, deserves our
support.
Admiral Vishnu Bhagwat may be contacted at
vbhagwat@bom7.vsnl.net.in.
Reproduced from:
http://www.thepowerhour.com/articles/du_effects.htm
Gulf War Veterans and Depleted Uranium
Prepared for the
Hague Peace Conference, May 1999
By Dr. Rosalie Bertell, Ph.D., G.N.S.H.
Source of Exposure:
Uranium metal is autopyrophoric and can burn
spontaneously at room temperature in the presence of air, oxygen and water. At
temperatures of 200-400 degrees Centigrade, uranium powder may self-ignite in
atmospheres of carbon dioxide and nitrogen. Oxidation of uranium under certain
conditions may generate sufficient energy to cause an explosion (Gindler
1973). Friction caused by bullet or missile entry into a tank or armored car,
for example, can cause the uranium to ignite, forming a concentrated ceramic
aerosol capable of killing most personnel in the vehicle. Depleted uranium was
used extensively in place of tungsten for ordnance by the US and UK in the
Gulf War.
There is no dispute of the fact that at least 320
tons of depleted uranium (DU) was "lost" in the Gulf war, and that much of
that was converted at high temperature into an aerosol, that is, minute
insoluble particles of uranium oxide, UO2
or UO3 , in a mist or fog. It would have been
impossible for ground troops to identify this exposure if or when it occurred
in war, as this would require specialized detection equipment. However,
veterans can identify situations in which they were likely to have been
exposed to DU. Civilians working at military bases where live ammunition
exercises are conducted may also have been exposed.
Uranium oxide and its aerosol form are insoluble in
water. The aerosol resists gravity, and is able to travel tens of kilometres
in air. Once on the ground, it can be resuspended when the sand is disturbed
by motion or wind. Once breathed in, the very small particles of uranium
oxide, those which are 2.5 microns [ one micron = one millionth of a meter ]
or less in diameter, could reside in the lungs for years, slowly passing
through the lung tissue into the blood. Uranium oxide dust has a biological
half life in the lungs of about a year. According to British NRPB [ National
Radiation Protection Board ] experiments with rats, the ceramic or aerosol
form of uranium oxide takes "twice as long" or about a two year biological
half life in the lungs, before passing into the blood stream. [Stradling et al
1988]
Because of coughing and other involuntary mechanisms
by which the body keeps large particles out of the lungs, the larger particles
are excreted through the gastro-intestinal tract in feces. The uranium
compounds which enter the body either through the wall of the
gastro-intestinal tract or the lungs, can be broken down in the body fluids,
and tetravalent uranium is likely to oxidize to the hexavalent form, followed
by the formation of uranyl ions. Uranium generally forms complexes with
citrate, bicarbonates or protein in plasma, and it can be stored in bone,
lymph, liver, kidney or other tissues. Eventually this uranium which is taken
internally is excreted through urine. Presence of depleted uranium in urine
seven or eight years after exposure is sufficient evidence to substantiate
long term internal contamination and tissue storage of this radioactive
substance.
Uranium is both a chemical toxic and radioactive
hazard: Soluble uranium is regulated because of its chemical toxicity,
measured by damage to the kidney and tubules. Uranium is a heavy metal, known
to cause uranium nephritis. Insoluble uranium, such as was released in the
Gulf War, is regulated by its radiological properties, and not its chemical
properties. Because of its slow absorption through the lungs and long
retention in body tissues, its primary damage will be due to its radiological
damage to internal organs rather than chemical damage to the renal system.
Obviously, both types of damage occur simultaneously, therefore it is a matter
of judgment which severe damage, radiological or chemical, occurs at the
lowest dose level. However, with the lengthening of the time during which the
contaminant resides in the body and the low overall dose, the risk of cancer
death becomes greater than the risk of significant damage to the renal system.
Uranium
decays
into other radioactive chemicals with statistical regularity. Therefore, in
its natural and undisturbed state, it always occurs together with a variety of
other radioactive chemicals, some of the best known being thorium, radium,
polonium and lead.
Natural uranium in soil is about 1 to 3 parts per
million, whereas in uranium ore it is about 1,000 times more concentrated,
reaching about 0.05 to 0.2 percent of the total weight. Depleted uranium
concentrate is almost 100 percent uranium. More than 99 percent of both
natural and depleted uranium consists of the isotope U-238. One gram of pure
U-238 has a specific activity of 12.4 kBq, which means there are 12,400 atomic
transformations every second, each of which releases an energetic alpha
particle. Uranium 238 has a half life of 4.51 E+9 (or 4.51 times 10 to the
9thpower, equivalent to 4,510,000,000 years).
Each atomic transformation produces another
radioactive chemical: first, uranium 238 produces thorium 234, (which has a
half life of 24.1 days), then the thorium 234 decays to protactinium 234
(which has a half life of 6.75 hours), and then protactinium decays to uranium
234 (which has a half life of 2.47E+5 or 247,000 years). The first two decay
radioisotopes together with the U 238 count for almost all of the
radioactivity in the depleted uranium. Even after an industrial process which
separates out the uranium 238 has taken place, it will continue to produce
these other radionuclides. Within 3 to 6 months they will all be present in
equilibrium balance. Therefore one must consider the array of radionuclides,
not just uranium 238, when trying to understand what happened when veterans
inhaled depleted uranium in the Gulf War.
It should be noted that uranium 235, the more
fissionable fraction which was partially removed in enrichment, makes up only
0.2 to 0.3 percent of the depleted uranium, whereas it was 0.7 percent of
natural uranium. It is this deficit which enables one to use analytical
methods to identify the uranium found in veteran's urine as depleted and not
natural uranium. The U 235 was extracted for use in nuclear weapons and
nuclear reactor fuel. Depleted uranium is considered nuclear waste, a
by-product of uranium enrichment.
The difference in radioactivity between natural and
depleted uranium is that given equal quantities, depleted uranium has about
half the radioactivity of the natural mixture of uranium isotopes. However,
because of the concentration of the uranium in the depleted uranium waste,
depleted uranium is much more radioactive than uranium in its natural state.
Uranium and all of its decay products, with the
exception of radon which is a gas, are heavy metals. Unlike some other heavy
metals which are needed in trace quantities by the human body, there is no
known benefit to having uranium in the body. It is always a contaminant.
Ingesting and inhaling some uranium, usually from food, is inescapable
however, in the normal Earth environment, and we humans basically take in, on
average, 5 Bq per year of uranium 238 in equilibrium with its decay products.
This gives an effective radiation dose equivalent to the whole body of 0.005
mSv. Using a quantitative measure, we normally ingest about 0.000436 g a
year.[UNSCEAR 1988, 58-59] This is a mixture of soluble and insoluble
compounds, absorbed mostly through the gut.
Regulatory limits recommended by the International
Commission on Radiological Protection [ICRP] assume that the maximum
permissible dose for members of the public will be the one which gives the
individual 1 mSv dose per year. This is in addition to the natural exposure
dose from uranium in the food web. Assuming that this dose comes entirely from
an insoluble inhaled uranium oxide, and using the ICRP dose conversion factor
for uranium 238 in equilibrium with its decay products, one can obtain a
factor of 0.84 mSv per mg, or a limit of intake of 1.2 mg (0.0012 g) per year
for the general public. This would give an added radiation dose of 1.0 mSv
from uranium, and an increase of almost 2.75 times the natural uranium intake
level. Nuclear workers would be allowed by the ICRP maximum permissible level,
to reach an annual dose of 20 mSv, comparable to an intake of 24 mg of
uranium, 55 times the normal yearly intake.
The US has not yet conformed to the 1990
international recommendations which were used for this calculation, and it is
still permitting the general public to receive five times the above general
public amount, and the worker to receive 2.5 times the above occupational
amount. The US may have used its domestic "nuclear worker" limits during the
Gulf War, if it used any protective regulations at all. The military manual
discusses the hazards of depleted uranium as less than other hazardous
conditions on an active battle field!
The maximum dose per year from anthropogenic sources
can be converted to the maximum concentration permissible in air using the
fact that the adult male breathes in about 23 cubic metres of air in a day [ICRP
1977]. The maximum permissible concentration in air for the general public
would be: 0.14 microgram per cu metre, and for workers: 2.9 micrograms per cu
m assuming the Gulf War situation of continuous occupancy rather than a 40
hour work week, and an 8 hour day. It is common in the US and Canada to refer
to 2000 pounds as a "ton", whereas the British "ton" is 2240 pounds. Both are
roughly 1000 kg. Just in order to understand the scale of the ceramic uranium
released in Desert Storm, at least 300 million grams were "lost", and
breathing in only 0.023 g would be equivalent to the maximum permissible
inhalation dose for a nuclear worker to receive in a year under the 1990
recommendations of ICRP.
Medical Testing for
Depleted Uranium Contamination:
Potential testing includes:
chemical analysis of uranium in urine, feces,
blood and hair;
tests of damage to kidneys, including analysis for
protein, glucose and non-protein nitrogen in urine;
radioactivity counting; or
more invasive tests such as surgical biopsy of
lung or bone marrow.
Experience with Gulf War veterans indicates that a 24
hour urine collection analysis shows the most promise of detecting depleted
uranium contamination seven or eight years after exposure. However, since this
test only measures the amount of depleted uranium which has been circulating
in the blood or kidneys within one or two weeks prior to the testing time,
rather than testing the true body burden, it cannot be directly used to
reconstruct the veteran's dose received during the Gulf War. However, this
seems to be the best diagnostic tool at this time, eight years after the
exposure.
Feces tests for uranium are used for rapid detection
of intake in an emergency situation, and in order to be useful for dose
reconstruction, must be undertaken within hours or days of the exposure. Blood
and fecal analysis are not advised except immediately after a known large
intake of uranium.
Whole body counting for uranium, using the sodium
iodide or hyper pure germanium detectors, is designed to detect the isotope
uranium 235, the isotope of uranium partially removed from depleted uranium.
For lung counting, again it is the uranium 235 which is detected, and the
minimum detection limit is about 7.4 Bq or 200 pCi. Since normally humans take
in only 5 Bq per year, this is not a very sensitive measure. Seven or eight
years after the Gulf War exposure, this method of detection is most likely
useless for veterans.
Routine blood counts shortly after exposure, or
during a chelating process for decontamination of the body are useful. This is
not a search for uranium in blood, but rather a complete blood count with
differential. This is done to discover potentially abnormal blood counts,
since the stem cells which produce the circulating lymphocytes and
erythrocytes are in the bone marrow, near to where uranium is normally stored
in the body. The monocyte stem cells in bone marrow are known to be among the
most radiosensitive cells. Their depletion can lead to both iron deficient
anemia, since they recycle heme from discarded red blood cells, and to
depressed cellular immune system, since monocytes activate the lymphocyte
immune system after they detect foreign bodies.
Hair tests need to be done very carefully since they
tend to reflect the hair products used: shampoos, conditioners, hair coloring
or permanent waves. Pubic hair would likely be the best material for analysis.
I am not aware of good standards against which to test the Uranium content of
hair, or how the analysis would differentiate between the various uranium
isotopes.
Testing of lymph nodes or bone on autopsy would be
helpful. However, invasive biopsies on live patients carry no benefit for the
patient and are usually not recommended because of ethical considerations
about experimentation on humans. If a veteran is recommended for bronchoscopy
for medical reasons, it would be advisable to also take tissue samples for
analysis for depleted uranium.
When chelation processes have been initiated the rate
of excretion of uranium in urine will be increased and there is a risk of
damage to kidney tubules. Therefore careful urine analysis for protein,
glucose and non-protein nitrogen in important. Some researchers have also
reported specifically finding B-2-microglobulinuria and aminoaciduria in urine
due to uranium damage.
Relating Depleted Uranium Contamination
with Observed Health Effects in Veterans:
There are two ways of documenting the radiological
health effects of a veteran's exposure to depleted uranium. The first, and the
one usually attempted in a compensation argument, would be to reconstruct the
original dose and then appeal to regulatory limits or dose-response estimates
available in the scientific literature. This methodology is not recommended
for the Gulf War veterans, because the uranium excretion rate seven or eight
years after exposure cannot be used to estimate the original lung and body
burden of depleted uranium. Moreover, no dose-response estimates for the
chronic health effects of such exposure are available from the literature, as
will be seen later in this paper. Recognized dose-response estimates for
radioactive materials are unique to fatal cancers (and even these are
disputed). It is not clear whether regulatory limits for exposure to ionizing
radiation apply in a war situation, or, if they do, whether the veteran should
be considered to have been "general public" or a "nuclear worker". Beyond
this, the question of whether international or US standards should be used for
a multinational situation needs to be addressed.
The second methodology would require ranking veterans
on an ordinal scale for their original exposure, based on their current
excretion rate of depleted uranium. This involves the reasonable assumption
that the original contamination, although not precisely measurable, was
proportional to the current excretion rate. The analysis of a 24 hour urine
sample, for example, could be rated on a specific research scale as having
"high", "medium" or "low" quantities of the contaminate. By collecting
detailed health and exposure data on each veteran, one can use biostatistical
methods to determine firstly, whether any medical problems show an increase
with the ordinal scale increase in exposure, determined through urine
analysis; and secondly, whether there is a correlation between the descriptive
accounts of potential depleted uranium exposure and the assigned ordinal scale
determined on the basis of the urine analysis.
Using Non-Parametric Statistics one could determine
the statistical significance of various medical problems being depleted
uranium exposure related. This would undoubtedly eliminate some medical
problems from consideration and highlight others. It could point to future
research questions. It could also provide a fair method of dealing with the
current suffering of the veterans using the best scientific methodology
available at this time. Risk estimates based on radiation related cancer death
are obviously unable to provide a reasonable response to current veteran
medical problems.
Known Occupational Health Problems
Related to Uranium Exposure:
In Volume 2 of the Encyclopaedia of Occupational
Health, under uranium alloys and compounds, page 2238, it reads:
"Uranium poisoning is characterized by generalized
health impairment. The element and its compounds produce changes in the
kidneys, liver, lungs and cardiovascular, nervous and haemopoietic systems,
and cause disorders of protein and carbohydrate metabolism.......
Chronic poisoning results from prolonged exposure
to low concentrations of insoluble compounds and presents a clinical picture
different from that of acute poisoning. The outstanding signs and symptoms
are pulmonary fibrosis, pneumoconiosis, and blood changes with a fall in red
blood count; haemoglobin, erythrocyte and reticulocyte levels in the
peripheral blood are reduced. Leucopenia may be observed with leucocyte
disorders (cytolysis, pyknosis, and hypersegmentosis).
There may be damage to the nervous system.
Morphological changes in the lungs, liver, spleen, intestines and other
organs and tissues may be found, and it is reported that uranium exposure
inhibits reproductive activity and affects uterine and extra-uterine
development in experimental animals. Insoluble compounds tend to be retained
in tissues and organs for long periods."
Human and Animal Studies on Uranium
Exposure:
In a study of uranium toxicity by the US Agency for
Toxic Substances and Disease Registry [ATSDR 1998], released for public review
and comments by 17 February 1998, exposure times were divided into three
categories: acute, less than 15 days; intermediate, 15 to 365 days; and
chronic more than a year. Most of the Gulf War Veterans would have had chronic
duration exposure from the point of view of the length of time the material
remained in the body. However, this ATSDR division was based of the duration
of the presence of the external source of contamination, not its residence
time in the body, therefore it would, in most cases be considered intermediate
duration exposure. There is very little human research available to clarify
the effects of intermediate duration exposure to humans.
It should not be assumed that lack of research
implies lack of effect on that particular system. It should also be noted that
although one or more papers may exist for acute and chronic duration
exposures, these do not necessarily cover the questions which one might like
to raise. No comments on the quality or extent of the research is implied by
this table.
Health Effects which have been
associated with inhalation of uranium:
The more soluble compounds of uranium, namely,
uranium hexafluoride, uranyl fluoride, uranium tetrachloride, uranyl nitrate
hexahydrate, are likely to be absorbed into the blood from the alveolar
pockets in the lungs within days of exposure. Although inhalation products
also are transported through coughing and mucocilliary action to the
gastro-intestinal tract only about 2 percent of this fraction is actually
absorbed into the body fluids through the intestinal wall. Therefore all of
the research papers on acute effects of uranium refer to these soluble uranium
compounds via inhalation. The main acute effect of inhalation of soluble
uranium compounds is damage to the renal system, and the main long term
storage place of these compounds in the body is bone.
These research findings do not apply easily to the
insoluble uranium compounds to which the Gulf Veterans were exposed when the
depleted uranium ordnance was used in battle.
The uranium compound used for ordnance was uranium
238 and limited amounts of its decay products. Particles of these compounds
smaller than 2.5 microns are usually deposited deep in the lungs and pulmonary
lymph nodes where they can remain for years. According to research done in the
UK by the NRPB, ceramic uranium is formed when uranium ignites through
friction, as happened in the Gulf War. In this form, it is twice as slow to
move from the lungs to the blood than would be the non-ceramic uranium. Of the
portion of inhaled uranium which passes through the gastro-intestinal tract,
only 0.2 percent is normally absorbed through the intestinal wall. This may be
an even smaller portion for ceramic uranium. This fraction of the inhaled
compound can, of course, do damage to the GI tract as it passes through
because it emits damaging alpha particles with statistical regularity. The
residence time of the insoluble uranium compounds in the GI tract (the
biological half life) is estimated in years. [ibid.]
The chemical action of all isotopic mixtures of
uranium (depleted, natural and enriched) is identical. Current evidence from
animal studies suggests that the chemical toxicity is largely due to its
chemical damage to kidney tubular cells, leading to nephritis.
The differences in toxicity based on the solubility
of the Uranium compound (regardless of which uranium isotope is incorporated
in the compound) are more striking: water soluble salts are primarily renal
and systemic chemical toxicants; insoluble chemical compounds are primarily
lung chemical toxicants and systemic radiological hazards. Once uranium
dioxide enters the blood, hexavalent uranium is formed, which is also a
systemic chemical toxicant.
It is important to note that there is no scientific
evidence which supports the US Veteran Administration claim that the insoluble
uranium to which the Gulf War Veterans were exposed will be primarily a renal
chemical toxicant. Yet this is the criteria which the VA proposes for
attributing any health problems of the Veteran to depleted uranium.
Intermediate and chronic exposure duration to insoluble uranium is regulated
in the US by its radiological property. The slow excretion rate of the uranium
oxide allows for some kidney and tubule repair and regeneration. Moreover,
because of the long biological half life, much of the uranium is still being
stored in the body and has not yet passed through the kidneys. The direct
damage to lungs and kidneys by uranium compounds is thought to be the result
of the combined radiation and chemical properties, and it is difficult to
attribute a portion of the damage to these separate factors which cannot be
separated in life.
There is human research indicating that inhalation of
insoluble uranium dioxide is associated with general damage to pulmonary
structure, usually non-cancerous damage to alveolar epithelium. With acute
duration exposure this can lead to emphysema or pulmonary fibrosis (Cooper et
al, 1982; Dungworth, 1989; Saccomanno et al, 1982; Stokinger 1981; Wedeen
1992). Animal studies demonstrate uranium compounds can cause adverse
hematological disturbances (Cross et al. 1981 b; Dygert 1949; Spiegel 1949;
Stokinger et al 1953).
Important information from a chart developed by ATSDR
[referenced earlier] is reproduced here, the reader will find all of this
information and the references in the original document.
Availability of Human or Animal Data
for the Presence of a Particular Health Effect
after Exposure via Inhalation to Insoluble Uranium
| Effect on body system studied: |
Effects of acute duration exposure (less than
15 days) |
Effects of intermediate duration exposure (15
days to 1 year) |
Effects of chronic duration exposure (more than
1 year) |
| Respiratory |
Human Studies:
rales, slight degeneration in lung epithelium; hemorrhagic lungs [1]
Animal Studies:
severe nasal congestion, hemorrhage; gasping in 100 percent [2] |
Animal Studies:
slight degenerative changes in lung;[3] pulmonary edema; hemorrhage;
emphysema; inflamation of the brochi; bronchial pneumonia; alveoli and
alveolar interstices; edematous alveoli; hyperemia and atelectasis.; lung
lesions; minimal pulmonary hyaline fibrosis and pulmonary fibrosis. [2] |
Animal Studies:
minimal pulmonary fibrosis [3] Lung cancer in dog [3] |
| Hepatic
|
|
Animal Studies:
moderate fatty livers in 5 of 8 animals that died; focal necrosis of
liver.[3] |
Animal Studies:
increased bromo-sulfalein retention [2] |
| Hematological |
Animal Studies:
increased macrophage activity; increased plasma prothrombin and
fibrinogen.[3] |
A (increased percentage myeloblasts and lymphoid
cells in bone marrow; decreased RBC; increased plasma prothrombin and
fibrinogen; increased neutrophils ; decreased lymphocytes) |
Animal Studies:
lengthened blood clotting time, decreased blood fibinogen [2] |
| Gastro-intestinal |
Human Studies:
anorexia, abdominal pain, diarrhea, tenesmus or ineffective straining, and
pus and blood in stool [1] |
|
Animal Studies:
anorexia; vomited blood; ulceration of caecum.[1],[6] |
| Renal |
Human Studies:
proteinuria, elevated levels of NPN, aminoacid nitrogen/creatinine, abnormal
phenol-sulfonphthalein excretion. Increased urinary catalase; diuresis.[1]
Animal Studies:
Proteinuria, glucosuria and polyuria; severe degeneration of renal cortical
tubules 5-8 days post exposure. [2] |
Animal Studies:
diuresis, mild degeneration in glomerulus and tubules. [3] proteinuria,
increased NPN.[3] minimal microscopic lesions in tubular epithelium [1]
|
Animal Studies:
slight azotemia [4] slight degenerative changes [3] minimal microscopic
lesions [1], [5],[6] tubular necrosis and regeneration [6] |
| Cardiovascular |
|
|
|
| Musculo-skeletal |
|
Animal Studies:
severe muscle weakness; lassitude [3 with F]. |
|
| Endocrine |
|
|
|
| Metabolic |
|
|
|
| Dermal |
|
|
|
| Ocular |
Animal Studies:
conjunctivitis [2] |
Animal Studies:
eye irritation [2] |
|
| Body Weight |
|
Animal Studies:
26 percent decrease inMetabolicght; 14 percent decrease at 22 mg / cu m air;
[1], [3] 12 percent decrease at 2.1 mg/cu m air.[2] 2.9 to 27.9 percent
decreased body weight guinea pig [6] |
|
| Other Systemic |
|
Animal Studies:
weakness and unsteady gate, [1] minimal lymph node fibrosis.[3] rhinitis [1] |
Animal Studies:
minimal lymph node fibrosis [3] lung cancer (dog) [3] |
| Mortality |
Animal Studies:
20 percent for dogs at 2 mg per cu. m air [2] Animal Studies:
10 percent rat and guinea pig [4] 17 percent dog [4] 60 percent rabbits [3]
67 percent rabbits [4] |
Animal Studies:
4.5 percent mortality dog [3] |
|
- Uranium tetrafluoride, UF4
, insoluble in water.
- Uranium hexafluoride, UF6
, soluble in water, highly chemically toxic.
- Uranium dioxide, UO2 ,
insoluble in water, highly toxic and spontaneously flammable, used in ordnance
in place of lead in the Gulf War. (Also called uranium oxide.)
- Uranium trioxide, UO3 ,
insoluble in water, poisonous, decomposes when heated. (Also called uranium
oxide.)
- Uranyl Chloride, UO2Cl2
, uranium oxide salt.
- Uranium Nitrate, UO2(NO3)2.2H2O
, soluble in water, toxic and explosive.
With respect to ORAL exposure, there is no human data
but a great deal of animal data. This was not as likely a pathway in the Gulf
War as was inhalation, but possible contamination of food and water can not be
totally ignored.
DERMAL exposure was researched in humans only in the
acute duration of exposure case. Animal studies on dermal exposure include
acute, intermediate and chronic duration of exposure, and immunologic/lymphoreticular
and neurologic effects.
Mortality Within 30 Days of Exposure:
The lowest acute duration lethal dose observed, with
exposure to the soluble uranium hexafluoride, was 637 mg per cu metre of air.
No acute dose deaths were found using insoluble compounds. Since there were
acute deaths in the Iraqi tanks in persons not directly hit, one can assume
concentrations of uranium aerosol were greater than this amount. It should
also be noted that it was the radiation protection units of the military which
designated these contaminated tanks off bounds. They were acting because of
radiological (not chemical) properties of the aerosol.
The intermediate duration exposure, 15 to 365 days,
dose level for mortality with insoluble uranium oxide, was 15.8 mg per cu
metre of air. With soluble uranium hexachloride it was much lower, 2 mg per cu
metre air.
The dose resulting in lung cancer in the dog study,
with chronic duration inhalation of the insoluble uranium oxide, was 5.1 mg
per cu metre air, for 1 to 5 years, 5 day a week and 5.4 hours a day.
Systemic Damage:
Damage to body organs occurred with intermediate or
chronic exposure at doses as low as 0.05 mg per cu metre air. A generally
sensitive indicator of exposure seems to be loss of body weight. However this
finding is somtimes attributed to the unpleasant taste of the uranium laced
food given to animals. There is also damage to the entrance portals:
respiratory and gastro-intestinal systems; and the exit portals: intestinal
and renal systems. Uranium oxide was associated with fibrosis and other
degenerative changes in the lung. It was also associated with proteinuria, and
increased NPN (non-protein nitrogen) and slight degenerative changes in the
tubules. The more severe renal damage was associated with the soluble
compounds uranium tetrafluoride and uranium hexafluoride (not thought to have
been used in the Gulf War ordnance).
Focal necrosis of the liver was only associated with
uranium oxide. This may be a clue to one of its storage places in body tissue.
Uranium oxide is also associated with hematological changes, lymph node
fibrosis, severe muscle weakness and lassitude at intermediate or chronic dose
rates in 0.2 to 16 mg per cu metre air. None of the uranium research dealt
with the synergistic, additive or antagonistic effects potentially present in
the Gulf War mixture of iatrogenic, pathological, toxic chemical and
electromagnetic exposures.
Potential US Government administration of
radio-protective substances to combat military:
It is obvious that the US had some expectation of the
health effects related to using depleted uranium ordnance in the Gulf War.
This is evident based on military research and manuals. They would also have
had access to information on chemical and biological agents which could
protect against some of the harmful side effects. These agents might also
"confuse" the toxicology of this exposure. Some potential radio-protective
agents are thiols (also called mercaptans, these are organosulfur compounds
that are derivatives of hydrogen sulfide), nitroxides (used as a food aerosol
and an anesthetic), cytokines (non-antibody proteins released by one cell
population, e.g T-lymphocytes, generating an immune response), eicosanoids
(biologically active substances derived from arachidonic acid, including the
prostaglandins and leukotrienes), antioxidants and modifiers of apoptosis
(fragmentation of a cell into small membrane bound particle which are then
eliminates by phagocytes).
Just in case this is the reality and not merely a
suspicion, it would be good to examine the after effects of exposure to
ceramic depleted uranium in Iraqi veterans and in the survivors of the El Al
crash at Shipol Airport, Amsterdam. It is unlikely that these two populations
were given any protective agents.
Proposal for assisting the Gulf War
veterans:
In keeping with the above findings, it is proposed to
undertake an analysis of both questionnaire and clinical data for a sample of
each of the following populations: US, Canadian and British Gulf War veterans
or civilian base workers exposed to DU; US, Canadian and British military
personnel not exposed to DU; Iraqi Veterans exposed to DU; Iraqi Veterans not
exposed to DU; and firemen and civilians exposed to the El Al crash.
Sampling strategy and sample size to be
determined:
Each participant should complete a questionnaire [See
draft questionnaire in Appendix A] covering general background variables,
exposure profile and medical problems and symptoms. Each participant will
agree to collect a 24 hour urine sample for analysis, and to take 500 mg
blue-green algae (Spirulina) 48 hours before beginning the collection. This is
a mild chelating agent. Each participant will agree to the analysis of this
data for the benefit of all exposed persons, and to the release of the results
of the analysis without identifying characteristics for individuals.
All questionnaire data will be entered into computer
using Epi Info Software (WHO) and transferred on disc to the Biostatistical
Support Unit of the University of Toronto for analysis.
Research Hypotheses to be tested:
(to be written as a null hypothesis)
There will be a high correlation between the
questionnaire exposure estimates and the level of depleted uranium found in
urine. Medical problems related to damage of the blood and/or hepatic systems
will show an association with exposure data and urine sample analysis for
depleted uranium.
Preliminary work to be accomplished:
- Identification of principal investigators for each
identified study group.
- Development of a Grant Proposal, including the
null hypotheses and protocols.
- Development of a budget for each population study
group.
- Agreement of the Research team to undertake the
study.
- Raising of funds or assignment of costs for the
study.
- Identification and training of data entry
processors for each group.
Benefits for Participants:
In addition to the general benefits to be obtained by
clarifying the health effects of exposure to this toxic material, especially
in the ceramic form experienced in the Gulf War, each participant testing
positive for DU in a urine analysis will be assisted to enter a chelating
process to remove as much as possible of the contaminant from the body.
References:
ATSDR 1998: "Toxicological Profile for Uranium" Draft
for Public Comment, US Department of Health and Human Services, Public Health
Service, Agency for Toxic Substances and Disease Ragistry, September 1997.
Cooper JR, Stradling GN, Smith H, et al 1982. "The
behaviour of uranium 233 oxide and uranyl 233 nitrate in rats. International
Journal of Radiation Biology and Related Studies in Physics, Chemistry and
Medicine. Vol 41(4): 421-433.
Cross FT, Palmer RF, Busch RH et al, 1981.
"Development of lesions in Syrian golden hamsters following exposure to radon
daughters and uranium dust". Health Physics Vol 41:1135-153.
Dungworth DL. 1989 "Non-carcinogenic responses of the
respiratory tract to inhaled toxicants." In: Concepts in Inhalation
Toxicology. Editors: McClellan RO, and Henderson RF. Hemisphere Publ. Corp.
New York NY.
Dygert HP 1949. Pharmacology and Toxicology of
Uranium Compounds. Pages: 647-652, 666-672, and 673-675. McGraw Hill Books
Inc.
Encyclopaedia of Occupational Health and Safety,
Third (Revised) Edition. Technical Editor: Dr. Luigi Parmeggiani, published by
the International Labour Organization in 1983 (ISBN: 92-2--103289-2) Geneva,
Switzerland.
Gindler JE, 1973. "Physical and Chemical Properties
of Uranium." In: Uranium, Plutonium and Transplutonic Elements" Editors: Hodge
et al. New York NY: Springer Verlag; 69-164.
ICRP 1991: Recommendations of the International
Commission on Radiological Protection. Publication, accepted in 1990 and
reported in Publication 60. Pergamon Press, UK.
Saccamanno G, Thun MJ, Baker DB, et al 1982. "The
contribution of uranium miners to lung cancer histogenesis renal toxicity in
uranium mill workers". Cancer Research Vol. 82 43-52.
Spiegel CJ, 1949. Pharmacology and Toxicology of
Uranium Compounds. McGraw Hill Book Co.Inc.
Stokinger HE, Baxter RC, Dygent HP, et al 1953. In:
Toxicity Following Inhalation for 1 and 2 Years. Editors: Voegtlin C and Hodge
HC.
Stokinger HE, 1981. Uranium. In: Industrial Hygiene
and Toxicology. Vol 2A, 3rd Edition. Editors:Clayton CD and Clayton FE. John
Wiley and Sons, New York NY, 1995-2013.
Stradling GN, Stather JW, Gray SA, et al. "The
metabolism of Ceramic Uranium and Non-ceramic Uranium Dioxide after Deposition
in the Rat Lung." Human Toxicology 1988 Mar 7; Vol 7 (2): 133-139.
UNSCEAR: United Nations Scientific Committee on the
Effects of Atomic Radiation reports to the UN General Assembly.
Wedeen RP, 1992. "Renal diseases of Occupational
Origin". Occupational Medicine Vol 7 (3):449.
Reproduced from:
http://www.ccnr.org/du_hague.html
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