Presented and Peer Reviewed at the EANM Congress 2007 -
Copenhagen, Denmark
The Quantitative Analysis of Uranium Isotopes
in the Population of Port Hope, Ontario Canada
Asaf
Durakovic, Axel Gerdes, Isaac Zimmerman
Uranium Medical Research Center
www.umrc.net
CURRICULUM VITAE
ASAF
DURAKOVIC, M.D., Ph.D., F.A.C.P
157
Carlton Street, Suite 206, Toronto, Ontario Canada M5A 2K3
Institute for Mineralogy, JW Goethe University, Frankfurt, Germany
Introduction
The contamination of the civilian population living in the vicinity
of nuclear fuel processing plants has been a subject of numerous studies
and controversy regarding the adverse effects of internal contamination
with uranium isotopes released into the environment. Among many sites
in North America, particular interest has been given to facilities such
as Fernald, Ohio and Paducah, Kentucky although they were never followed
up by objective research studies of the quantities and ratios of uranium
isotopes. Likewise the oldest uranium processing facility in the world,
located in Port Hope, Ontario Canada, although being studied by epidemiological
research, the objective analytical study of uranium isotopes in the
Port Hope population has never been conducted. The purpose of our study
was the quantitative analysis of the internal contamination with four
uranium isotopes in the population living near the uranium conversion
facility in Port Hope, Ontario Canada.
Port Hope harbor back dropped by the Cameco facility, UF6 drums are
visible behind the fence
Materials and Methods
The urine samples of subjects presenting with multi-system, non-specific
symptoms of immune system alterations, musculo-skeletal, central nervous
system, and neoplastic disease were obtained from residents of Port
Hope and analyzed in reference to the control samples from residents
of other parts of Ontario. The samples were analyzed at the Institute
for Mineralogy, J.W. Goethe University, Frankfurt, Germany in a specialized
radiochemistry laboratory by mass spectrometry. The analytical methodology
included pre-concentration of urine by co-precipitation, oxidation of
organic matter, uranium purification by ion-exchange chromatography,
and ICP-MS double-focusing Thermo Finnigan Neptune multi-collector.
Results
Our results show 4 of 9 samples containing uranium of nonnatural origin.
Subject 3 was highly positive for depleted uranium with a 238U/235U
ratio of 147.11 ± 1.42 and a relatively normal abundance of total
uranium. This sample contained a concentration of 236U with a 236U/238U
ratio of 4.38 x 10-6 ± 4.3 x
10-7 indicating its reactor origin. Three other subjects (2, 4, and
6) contained detectable amounts of 236U. Subject 6 had a paradoxically
high 236U/238U ratio of 5.53 x 10-5 ± 3.9 x 10-6. Subject 2 also
had a higher than normal concentration of total uranium at 24.8 ng/L.
The 236U in these samples indicates its origin as contamination with
non-natural uranium. The remaining five subjects were negative for both
depleted uranium and uranium- 236. Control subjects had no detectable
236U and a normal concentration of total uranium in their urine. Control
subject 2 had a natural 238U/235U ratio. However control subject 1 had
238U/235U ratio that was slightly depleted. It was learned after testing
that this person had visited Port Hope at some time prior to giving
their sample.
Mass spectrometry lab data:
238U/235U Isotopic Ratio, Total Uranium, and 236U Concentration
|
Subject
|
238U/235U
|
2
SD
|
U
ng/L
|
236U
fg/L
|
|
1
|
137.97
|
0.31
|
8.5
|
<1
|
|
2
|
137.99
|
0.57
|
24.8
|
1.7
|
|
3
|
147.11
|
1.42
|
7.0
|
31
|
|
4
|
138.75
|
1.12
|
5.1
|
<1
|
|
5
|
139.26
|
1.52
|
2.7
|
<1
|
|
6
|
137.71
|
0.67
|
9.4
|
517
|
|
7
|
138.22
|
0.83
|
8.8
|
<1
|
|
8
|
138.49
|
1.79
|
3.0
|
<1
|
|
9
|
137.34
|
0.78
|
3.7
|
<1
|
|
Control
1
|
138.74
|
0.41
|
5.6
|
<1
|
|
Control
2
|
138.14
|
1.54
|
2.1
|
<1
|
Mass
spectrometry lab data:
234U/238U and 236U/238U Isotopic Ratios
|
Subject
|
234U/238U
|
2
SD
|
236U/238U
|
2
SD
|
|
1
|
6.71
x 10-5
|
8.88
x 10-6
|
|
|
|
2
|
5.65
x 10-5
|
1.11
x 10-6
|
6.53
x 10-8
|
8.6
x 10-9
|
|
3
|
5.17
x 10-5
|
5.03
x 10-6
|
4.38
x 10-6
|
4.3
x 10-7
|
|
4
|
6.78
x 10-5
|
9.43
x 10-6
|
7.48
x 10-8
|
4.3
x 10-8
|
|
5
|
6.81
x 10-5
|
5.06
x 10-6
|
|
|
|
6
|
5.97
x 10-5
|
4.69
x 10-6
|
5.53
x 10-5
|
3.9
x 10-6
|
|
7
|
6.01
x 10-5
|
4.50
x 10-6
|
|
|
|
8
|
5.56
x 10-5
|
7.09
x 10-6
|
|
|
|
9
|
7.07
x 10-5
|
3.16
x 10-6
|
|
|
|
Control
1
|
4.80
x 10-5
|
9.82
x 10-7
|
|
|
|
Control
2
|
4.62
x 10-5
|
5.50
x 10-6
|
|
|
A
street, private home, and childrens playground in the immediate
vicinity of the Cameco facility;
a tarp covers uranium tailings
Discussion
The inadvertent exposure and toxicology of uranium isotopes in both
military personnel and civilians employed in the nuclear industry or
living in the vicinity of uranium processing plants has been well documented.
Both parenteral and oral administration of uranium isotopes has been
studied in animal
studies and humans. Of particular interest are inhalational pathway
toxicity studies which confirmed significant renal and pulmonary damage
with eleven uranium compounds including oxides, fluorides, tetrachlorides,
and nitrates in six different animal species as well as humans. Most
recent studies of the
Gulf War veterans have estimated a significant carcinogenic risk of
inhaled depleted uranium. Uranium containing dust has been identified
as the most important source of radiation exposure in uranium mining
and processing. Toxicity of uranium in the ground waters (Saskatchewan,
Canada), higher risk of lung cancer in uranium miners (New Mexico, Arizona),
overall cancer risk in workers involved in the uranium processing industry
(Ohio, Colorado), and numerous published studies from around the world
all point to the realistic probability of adverse health effects of
uranium isotopes in the human population living in the vicinity of nuclear
processing plants.
Summary
The
contamination with depleted uranium has been verified and well documented
in the studies on the military personnel in the conflicts in Iraq and
Eastern Afghanistan, as well as, in the civilian population. The history
of uranium contamination in Port Hope is well documented. Our results
provide the first objective analytical study of long-term contamination
and possible association with adverse health effects in the current
population of Port Hope. These preliminary results warrant additional
multidisciplinary studies.
History of the Nuclear Industry in Port Hope
Canada began mining uranium ores in the early 20th century for their
radium content. In 1930, uranium ores were discovered in the Great Bear
Lake deposit in the North West Territories and were developed by Eldorado
Gold Mines for radium and uranium extraction. The refinery in Port Hope,
Ontario was the first facility of its kind built and the only one in
North America in the early 1940s that was equipped to refine uranium.
Uranium concentrates (yellowcake) were shipped to the refinery where
uranium was refined
into uranium oxides (UO2 and UO3) as well as uranium hexafluoride (UF6).
From 1941 to 1945, the entire production of refined uranium was supplied
to the United States for use in the Manhattan project. The Port Hope
facility had hundreds of tons of uranium concentrate on site from years
of radium extraction but to meet demand Eldorado reopened the mine at
Great Bear Lake which had shut down two years earlier. The facility
also refined uranium from ores purchased by the US from Union Minière,
a Belgian company that developed a deposit in the African Congo. Canadas
uranium mining and processing industry continued to sell uranium for
nuclear weapons until 1959 when United States stopped purchasing uranium
from Canada. Production slowed but continued under the Canadian governments
uranium stockpiling program until the mid 1980s. Eldorado Nuclear built
a new uranium refinery at Blind River, Ontario (early 1980s). The Blind
River facility refined uranium concentrate into UO3 which was shipped
to Port Hope. In Port Hope, UO3 was converted into UO2 and UF6. The
UO2 was then sold as fuel for CANDU reactors. The UF6 was exported to
enrichment facilities. The Port Hope facility also produced depleted
uranium metals until 1992 and processed enriched uranium from 1966 to
1987. Port Hope also blended enriched and depleted uranium powders to
specific isotopic concentrations. In 1988, Cameco Corporation was formed
by the privatization of Canadas uranium industry and the merger
of two government owned corporations Eldorado Nuclear and Saskatchewan
Mining Development Corporation. Cameco is the only Canadian company
and one of only four companies currently providing uranium refining
and conversion services to the western world; the other three being
Honeywell in the United States, British Nuclear Fuels Limited in the
United Kingdom, and Comurhex in France. Cameco is the worlds largest
uranium producer with four operating mines in Canada and the United
States and two new mines being developed, one in Canada and the other
in Central Asia. It has about 40% of the capacity in the western world
to produce UF6. It is also the only producer of ceramic uranium oxides
for fuel in Canadianbuilt CANDU reactors.
Port Hope is also home to a facility established in 1965 to develop
fuel to support Canadas nuclear energy program. This facility
produces fuel pellets from refined UO2 and assembles fuel bundles for
CANDU reactors. In 2006, the plant was acquired by Cameco from Zircatec
Precision Industries.

Two UF6 drums left on a trailer in a publicly
accessible parking lot

Street
in Port Hope with UF6 drums just on the other side of the fence
VIEW
COMPLETE PEER REVIEWED STUDY HERE
Peer
review conducted by European Association of Nuclear Medicine
Copenhagen, Denmark 2007
|
A
joint project of
The Port Hope Community Health Concerns Committee (PHCHCC)
and Uranium Medical Research Centre (UMRC)
Application for Consideration
This application has been developed for use by individuals who have
reason to believe that they may have been contaminated by uranium as
a result of living, working or spending time in Port Hope, Ontario and
wish to apply to participate in the Port Hope Radiobiological Studies
Project. Exposure and contamination may have occurred as a result of
inhalation, skin absorption or ingestion of uranium and uranium compounds
present in the environment or any facility in Port Hope. It may be current,
recent or historical exposure caused by current, recent or historical
events, locations or materials.
If you are eligible,
you will proceed through the following steps:
1. Intake Interview
2. Clinical Assessment
3. Uranium Bioassay
Your application
will be reviewed by the project staff. We will contact you to discuss
your eligibility for proceeding to a clinical assessment and uranium
bioassay. If accepted you will receive a clinical assessment by a physician
specializing in internal contamination by radio nuclides. A 24-hour
specimen of your urine will be collected and examined in a mass-spectrometry
laboratory to determine if you are excreting unusual quantities (abundance)
and or types (isotopes) of uranium. You will receive a bioassay report
explaining the lab results and their interpretation. A consultation
can be provided to your personal physician. Patient participants may
be offered an opportunity to participate in follow-on studies of internal
contamination effects.
The clinical data
from all participants in the study will be used in scientific papers,
which will be submitted for review by other scientists, physicians,
presented at scientific conferences and published. The identity of all
patients and study participants will be kept confidential. As a participant
in the project you are deemed a patient of UMRC's consulting physicians
and you are protected by the rules of doctor-patient confidentiality.
The Port Hope Community
Health Concerns Committee will use the study results / data and UMRC's
analysis of the data for purposes of public information and planning.
The identity of all participants and patients will be kept confidential
to the project team. Selected project staff members designated within
the PHCHCC executive may have access to individual patient information
under the auspices of UMRC's physicians. Patients can choose to reveal
their own identities publicly or to others.
I would like to know if I am contaminated and I wish to participate
You may contact the Port Hope Community Health Concerns Committee (PHCHCC)
to discuss applying to the Radiobiological Studies Project being offered
by the Committee and the Uranium Medical Research Centre (UMRC), by
sending an e-mail to the address below or you may proceed to submit
a completed application in writing to the Committee at the address provided.
To
recieve a copy of the "Application for Consideration"
for the PORT HOPE RADIOBIOLOGICALSTUDIES PROJECT 2005
Email the PHCHCC
at info@porthopeconcerns.com
to recieve a
printable PDF version
or
to make a DONATION
please click here
Inquiries and Contact Information
All inquiries
are confidential
Local Contact
Port Hope Radio-biological Studies Project
Port Hope Community Health Concerns Committee
Box 476
Station Main
Port Hope, Ontario, Canada
L1A 3Z3
Email to Port
Hope Community Health Concerns Committee:
info@porthopeconcerns.com
UMRC Website:
www.UMRC.net
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