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To: The Canadian Nuclear Safety Commission (CNSC)
Commission Operations Officer
E-mail: interventions@cnsc-ccsn.gc.ca
Fax: (613) 995-5086
From: The Canadian Coalition for Nuclear Responsibility (CCNR)
c/o Gordon Edwards, President
E-mail: ccnr@web.ca
Fax: (514) 489-5118
Date: April 19 2005
Re: Environmental Assessment Guidelines re Bruce A
Refurbishment for Life Extension and Continued
Operations Project
CCNR is saddened but not surprised by the fact that CNSC staff
has dismissed all intervenors' comments and recommendations
regarding possible improvements to the environmental
assessment guidelines for the Bruce A Refurbishment for
Life Extension and Continued Operations Project.
Many of these comments related to the extraordinarily high
radiation fields and the unusual degree of radioactive
contamination in the environment to which workers
will be exposed in order to achieve the goals of the corporation.
Many of the comments related to the meager opportunities
for citizens and non-governmental organizations to undertake
a meaningful review of this gargantuan project, due to the
CNSC Staff's intention to deny any opportunity for an
independent panel hearing, consequently the absence of
intervenor funding, combined with the CNSC Staff's
determination to roll several large projects (the refurbishment
of units 1 and 2, the eventual retubing of units 3 and 4, and the
switch from natural uranium fuel to slightly enriched fuel) into
one low-level environmental screening review.
It has been the experience of CCNR and other organizations that
independent environmental assessment panels often do a much
more thorough job of investigating the prospects for off-site
environmental impacts and listen more attentively to alternate
points of view and to analyses presented by non-proponents than
is the case in a low-level screening review. Environmental panels
often issue recommendations that incorporate information derived
from a close and detailed scrutiny of the proponent's plans by other
intervenors in the hearings process. Members of the public and
non-governmental organizations are able to address themselves
more assiduously to the task of developing responsible critiques
when they know that the panel is open to entertaining such
critiques and when funding is available to finance a small but
meaningful amount of independent research on the dossier.
None of these conditions apply to the CNSC screening review
process.
Despite the fact that workers will be carrying out a
mini-decommissioning job without the benefit of the 30 to 40-year
"cooling-off" (dormancy) period universally recommended for the
final decommissioning of a CANDU reactor ; despite the fact that
the pressure tubes and calandria tubes will be more radioactive
for a greater period of time than any other waste materials ever
removed from the Bruce NGS (other than irradiated fuel) ; despite
the fact that the four massive steam generators, with 5000
radioactively contaminated pipes inside each one, have never
before been removed from a CANDU reactor; despite the fact that
steam generator removal will require a major breach of the
containment envelope of the plant, thereby posing an
unprecedented risk of environmental contamination; despite the
fact that there are as yet no acceptable facilities for the long-term
(i.e. permanent) management of such radioactive waste materials
(pressure tubes, calandria tubes, steam generators, etc.) ; despite the
fact that the longevity of the toxicity of these wastes exceeds the
entire span of recorded human history; nevertheless there is no
recommendation from the CNSC staff for a full independent
panel review of the project.
CNSC Staff seems to take a "business as usual" attitude which is
wholly inconsistent with the enormity of what is being proposed.
To maintain that such extraordinary activities carried out in such
exceptional circumstances are already covered by the normal
operating licence of the station appears to us to be stretching
credibility to the breaking point.
As stated in the Preliminary Decommissioning Plan for the
Gentilly 2 Nuclear Generating Station prepared for Hydro-Quebec
by TLG Services, Inc. in April 2001
(Document No. H08-1374-003, Rev. 0):
"Decommissioning work is inherently different from operating
a nuclear power station. By its very nature, decommissioning
activities tend to create dispersible contamination and break
down the safety and confinement barriers that were engineered
into a power plant's design. As such, . . . planning must account
for this and incorporate alternate methods to control these
hazards...." [sec. 6, p. 14]
We are quoting from the G-2 Preliminary Decommissioning
Study because it is close at hand. We are certain that similar
comments would apply to the Bruce reactors.
CCNR urges the Commissioners to call for separate consideration
of the steam generator removal operation from start to finish,
including the stabilization of the 5000 or more radioactively
contaminated tubes inside each steam generator, the breach of
containment required to lift the steam generators out through
the roof, the restoration of the containment shell to its original
state, and the packaging and storage of the steam generators once
they have been removed. This part of the assessment should
also consider accident scenarios such as dropping a steam generator.
Radiation fields and radioactive contamination levels are highest
for the pressure tubes and calandria tubes than for any other
components in the core area of the reactors or in the Primary Heat
Transport system. Immediately after shutdown, these radiation
levels are about 100 times greater than they would be after a 40-year
"cooling-down" (dormancy) period as recommended for a full
decommissioning job. In terms of worker exposure, the G-2
Preliminary Decommissioning Study states:
"Hydro Québec has chosen the deferred removal decommissioning
strategy to minimize both the occupational radiation dose to the
decommissioning staff and any potential exposure of the public.
The radiological hazards encountered during the decommissioning
of the reactor would principally be caused by radionuclides
produced during operation. The majority of this radioactivity at
station shutdown will be short-lived radionuclides such as
H-3 [tritium], Fe-55 [radioactive iron], Nb-95 [radioactive niobium],
Zr-95 [radioactive zirconium], and Co-60 [radioactive cobalt]. These
radionuclides will decay with time. If dismantling is delayed for
a sufficient period, dismantling crews will be exposed to lower
radiation fields. Cobalt-60, a strong gamma emitter, will become
the dominant radiation source after about four years of shutdown.
With radiation fields from Cobalt-60 decreasing by about a factor
of two every 5,26 years, a 34-year dormancy period will reduce the
radiation levels to which decommissioning workers will be
exposed by a factor of about 88." [Sect. 4, page 1]
"The AECL study ... estimated the occupational radiation exposure
that would be incurred by decommissioning a generic
[ CANDU 600 ] plant with 50 and 100-year dormancy periods....
However, the Gentilly decommissioning work is envisioned to
commence after a dormancy period hypothetically assumed to
be about 30 years. Therefore, the estimated radiation exposure
for the work performed after the dormancy period would require
adjustment [upwards] to reflect a larger radioactive inventory
and the resulting higher radiation fields ...." [Sect.6, page 15]
CCNR urges the Commissioners to recommend a full and
independent panel review of this project because of the
magnitude and import of the work itself, because of the intensity
of the external radiation fields confronted by the work force,
because of the extraordinarily high level of radioactive
contamination involved (including radioactive dust and
corrosion products), because of the unusual opportunities for
spreading contamination through the segmenting and volume
reduction operations, and because of the lack of detailed plans
for the long-term management of the refurbishment wastes,
which will remain dangerously radioactive for tens of thousands
of years.
In terms of environmental impact, contamination of the
atmosphere and the workers themselves with radioactive dust
and corrosion products is one of our major concerns. We recall
the circumstances in which workers at Pickering (during a
retubing operation) tracked radioactive carbon-14 dust home
over a period of weeks before it was detected. When the
contamination was discovered, bedsheets and furniture had
to be confiscated from those homes and disposed of as
radioactive waste. Recently (December 2004, during an
unusually extended maintenance outage) three contract
workers were radioactively contaminated at Gentilly-2.
We understand that there will be hundreds of contract workers
employed during the Bruce refurbishment. They will not be
working in a normal operational environment, but one with
much greater opportunity for inadvertent contamination As
the G-2 Preliminary Decommissioning Report states:
"Ambient radiation levels need to be as low as possible to
prevent false-positive indications of contamination and/or
contamination masked due to degraded detection sensitivity.
Additionally, it is important to eliminate any potential of
recontaminating a decontaminated area by first removing
all other sources of contaminants. This will reduce occupational
radiation exposure and minimize the need to rework, which
can prolong worker exposure to radiation and risk of industrial
type accidents...." [sec. 6, p. 14]
CCNR urges the Commissioners to reflect on the legislative
mandate of the CNSC which is to regulate the nuclear industry
so as "to prevent unreasonable risk to the environment and to
the health and safety of persons". We believe that great
attention must be paid to the prevention of inadvertent
radioactive contamination of persons and of the environment.
CCNR had direct experience with the health effects of radioactive
contamination in the person of Bjarnie Hannibal Paulson, who
was one of 80 RCAF instructors to be sent to Chalk River to
supervise some 600 raw Canadian army recruits from Camp
Petawawa in the radioactive cleanup of the NRU reactor building
which was contaminated with airborne and surface radioactivity
following an accident in 1958.
Corporal Paulson wore protective clothing and a charcoal respirator
during his time inside the contaminated area, but -- despite being
sent back to the showers three times to get rid of contamination
detected by the monitors -- he ended up years later with a medically
inexplicable pattern of hundreds of skin cancers all over his body,
including his anus and peri-anal region, which medical specialists
are quite certain was caused by radiation exposure. A well-known
skin pathologist at the Jewish General Hospital in Montreal, Dr.
Herb Srolowicz, found strong evidence of radiation damage in Mr.
Paulson's hair follicles, some of which were enlarged by as much
as a factor of 50 over a normal-sized hair follicle. When Dr.
Srolowicz showed the slides of Mr. Paulson's skin abnormalities
to other skin pathologists at international conferences, it was
evident that none of them had ever seen anything like it before.
Dr. Karl Morgan, known as the father of Health Physics and an
ex-officio member of the ICRP for many years, came to Montreal
to testify in Mr. Paulson's case. He was of the opinion that mote-like
radioactive particles may have been trapped in Mr. Paulson's hair
follicles for a considerable period of time, escaping detection from
the monitors and yet causing thousands of rems of exposure to Mr.
Paulson's basal cells. He demonstrated to the three judges in the
tribunal hearing Mr. Paulson's case, using a geiger counter and a
radioactive source, that even a conscientious scanning of Mr.
Paulson's body with a hand-held monitor could easily miss the
residual radioactive contamination that likely caused his skin
cancers.
Mr. Paulson had to endure seven separate hearings before he was
finally awarded compensation for his radiation injuries -- but only
after the case went to the Federal Appeals Court. In all that time,
there was absolutely no effort on the part of AECL (Atomic Energy
of Canada Limited, owner and operator of the NRU reactor) or the
AECB (Atomic Energy Control Board, the regulating agency at the
time) to talk to Mr. Paulson or his doctors, to examine Mr.
Paulson's unusual skin damage or his medical records, or to
monitor the health of the other 679 people who had been exposed
to unusual radioactive contamination levels during the 1958
cleanup.
CCNR recommends that the Commissioners require the licensee
to conduct a thorough life-time medical follow-up of all contract
workers and employees engaged in the refurbishment operations,
correlated with as much information as possible on the radiation
exposures and possible radioactive contamination episodes
associated with each individual worker.
As the recent CERRIE Report from Britain (Committee Examining
Radiation Risks of Internal Emitters, October 2004) indicates, there
is still a lot of uncertainty about the health effect of radiation, and
the appropriate risk factors may in some cases be underestimated
by a factor of 10, especially in cases of radioactive contamination.
Without collecting data on the actual subsequent health problems
of exposed individuals, there is no way that one can come to any
realistic appreciation of what those risks truly are. Health risks
are neither detected nor prevented by mathematical calculations
carried out by health physicists.
During the bygone days of the Atomic Energy Control Board, CCNR
and many other external commentators and non-governmental
agencies lamented the incestuous relationship between the
regulatory agency and the industry that it was supposed to be
regulating. The fact that most of the AECB staff came from the
very corporations that were supposed to be regulated by the AECB,
and the fact that AECB often operated in a secretive fashion,
seemingly in collusion with the nuclear industry, was a distressing
reality. More often than not, the AECB seemed to reinforce the
industry's litany of bland reassurances as to the "minimal" health
and environmental impacts of radioactive contamination or the
radiation exposure of persons. As long as such exposures or such
contamination were within regulatory limits, the implication was
that there was no rational basis for concern. This, despite the
existence of a great deal of clear scientific evidence that such
regulatory limits offer no absolute protection whatsoever against
various life-threatening and non-life threatening ailments.
For example, in 1978 CCNR published a simple analysis showing
that the AECB maximum permissible levels of radon gas in new
homes in the Elliot Lake area (0.02 WL), if experienced over a
lifetime in a large number of homes, would be expected to lead
to a 31 percent increase in lung cancer rates. That translates into
an additional 17 lung cancer deaths per thousand (over a lifetime),
additional to the 54 lung cancer deaths per 1000 (over a lifetime)
which was the published Ontario norm at that time. The AECB
refused to credit these calculations, despite its lack of expertise in
this area.
In 1980, the British Columbia Medical Association published a
lengthy (500 page) document in which the authors (Robert
Woollard, M.D., and Eric Young, M.D.) supported the CCNR
figures with additional calculations from other experts leading
to much the same conclusion as the CCNR's. The BCMA was
so disdainful of AECB's unscientific assertions to the contrary
that they entitled Chapter 22 of their report, "AECB : Unfit to
Regulate".
Subsequently, the AECB hired an independent epidemiologist
at McGill University, Duncan Thomas, Ph.D., to do a thorough
review of existing epidemiological evidence from several
different countries including Canada, and come up his best
estimate of the lung cancer risk factor for radon gas in homes.
His report indicated that the 0.02 WL standard for new homes
would be expected to lead to about a 40 percent increase in lung
cancer rates. The Duncan Thomas report also showed that the
permissible level of radon exposure for uranium miners,
4 WLM/year, could lead to a quadrupling of lung cancer rates
if every worker experienced that level of exposure over a
working lifetime. This is hardly a "safe level" of exposure!
Dr. Thomas' findings were fully confirmed in subsequent
publications of the US BEIR Committees.
CCNR urges the Commissioners to ensure that all workers
employed in refurbishment activities are fully informed about
the health risks associated with radiation exposure; in particular,
that to ensure that they are made to understand clearly that
regulatory guidelines do not provide any assurances that such
health effects as cancer may not subsequently be experienced
as a result of radiation exposure.
When the Nuclear Safety Act was proclaimed, it was stated in
Canadian Law for the first time that the primary function of the
regulatory agency was to regulate the nuclear industry so as "to
prevent unreasonable risk to the environment and to the health
and safety of persons", in addition to the over-riding goal of
safeguarding national security. The original Atomic Energy Act
made no specific mention of the safety of persons or of risks to
the environment.
CCNR was initially hopeful that an agency truly committed to
fulfilling this legislated mandate would begin to regard its true
constituency as being, not the technologists in the nuclear industry
and the bureaucrats who promote nuclear power, but the workers
and citizens that might be adversely affected by this industry, along
with the plants, animals, birds, fish, and other life forms that might
be forced to live in an increasingly contaminated environment.
This is apparently not the case with the Canadian Nuclear Safety
Commission, judging by the dogged determination of CNSC staff
to keep public input at a minimum, pro forma, unfunded level,
and to overwhelm the meager resources of non-governmental
intervenors by rolling several large and complex projects involving
enormous inventories of radionuclides into one low-level
environmental screening process.
According to the G-2 Preliminary Decommissioning Report,
referring to an AECL Conseptual Decommissioning Study
published some years earlier:
"The AECL study estimated a total of 851 TBq
[ = 851 terabecquerels = 851 trillion becquerels
= 851, 000, 000, 000, 000 disintegrations per second]
of long-lived activation products in the reactor components
and nearby structures at shutdown...."
"The total estimated inventory of long-lived fission products
to be present within the HTS and auxiliary systems was 9,24 TBq "
[ that's 9 trillion 240 billion becquerels = 9, 240, 000, 000, 000
disintegrations per second ] ....
"The HTS and moderator systems will be filled with heavy water
at the time of reactor shutdown in 2010. The most significant
radioactivity contained in this water will be tritium.... This
represents a total Tritium inventory of 6,03 E8 GBq."
[ i.e. 603 quadrillion becquerels = 600, 000, 000, 000, 000, 000
disintegrations per second] [Sect. 3, pp. 2-3]
CCNR requests CNSC Staff to determine and to report the
corresponding radioactive inventories associated with the
Bruce 1 & 2 reactors prior to refurbishment, and those associated
with the Bruce 3 & 4 reactors prior to retubing them.
CCNR recommends that the Commissioners disentangle the
different projects from one another and to insist on a separate
environmental assessment process for each one; viz. the
refurbishment of Units 1 and 2 ; the retubing of Units 3 and 4;
and the eventual use of Slightly Enriched Uranium Fuel.
With regard to the use of SEU (slightly enriched uranium) fuel,
CCNR has observed that the term SEU is not used by CNSC staff,
who prefer to use the term LVRF (low void reactivity fuel) or
"New Fuel". CCNR requests a specific clarification on this matter,
Is LVRF synonymous with SEU, or is it not? Is it possible that
LVRF might refer to any type of "new fuel" that has certain
characteristics in common with SEU, and if so, what precisely
are those characteristics? In particular, would the designation
LVRF apply to any suitably constituted version of MOX (mixed
oxide) fuel, utilizing some isotope(s) of plutonium rather than
uranium-235 as the fissile material in the fuel? Would CNSC
staff object to replacing the term LVRF throughout its document
with the term SEU. and if so, what would be the nature of the
objection?
As for the refurbishment and retubing operations, it is clear tO
CCNR that the best way "to prevent unreasonable risk to the
environment and to the health and safety of persons" and the
best way to keep radiation exposures "as low as reasonably
achievable" is to wait for several decades before carrying out
the mini-decommissioning activities proposed by Bruce Power.
In terms of regulatory leadership, it is clear to CCNR that these
complex refurbishment activities, set in an extraordinarily
intense radiation field, should not take place until specific
guidelines and regulations have been elaborated by the
regulatory agency to ensure that everything possible is done
to minimize radiation exposures and prevent radioactive
contamination of persons and the environment.
It is also clear to CCNR that it is not responsible for CNSC to
allow Bruce Power to produce an entirely new category of
radioactive waste -- namely the scrapped pressure tubes,
calandria tubes, and other refurbishment wastes, which are
second in radioactive intensity and longevity only to the
irradiated fuel itself -- before there is any realistic plan to
manage these wastes for the indefinite future, bearing in
mind that these wastes will remain dangerously radioactive
for a period of time longer than the span of recorded human
history.
CCNR hopes that in future, the CNSC will develop a superior
expertise in the fields of radiation effects (medical effects of
radiation exposure) and radio-ecology, given that the primary
mission of CNSC is supposed to be "to prevent unreasonable
risk to the environment and to the health and safety of
persons". After all, it is intended to be a "Safety" Commission,
not an "Industry" commission. The emphasis on safety as
opposed to industrial output is not apparent when the CNSC
staff continues to make comments such as this one:
Comment by Shawn-Patrick Stensil, Sierra Club of Canada:
"... rebuilding the Bruce A reactors closely resembles the
undertakings and projects listed under CEAA's Comprehensive
Study List Regulations for Nuclear and Related Facilities. This
evaluation should, then, be a Comprehensive Study. The fact
that the current guidelines exclude retubing activities from the
scope of the present screening level review is unacceptable."
CNSC Staff response:
"Staff is satisfied that the undertaking is the continued operation
of existing reactors for an extended period of time once refurbished.
None of the activities identified in the scope of the project would
change the original intent or operation of the Bruce A reactors.
Further, there is no intent to increase the originally installed net
electrical maximum continuous rating of 769 MW for each of the
four Bruce A reactors."
Does one need to have a change in the intent of an industrial
enterprise in order to have an environmental impact? Does
cutting, removing and compacting thousands of radioactively
contaminated pipes, and lifting 50-tonne steam generators out
through a hole in the roof of the containment building, not
represent a dramatic change in the routine operation of the
Bruce A reactors?
Where is the Staff concern for radiation damage to workers or
to the public? Where is the Staff concern for radioactive
contamination of the environment? Are these not the primary
concerns that are stated in law as the main justification for the
very existence of the Canadian Nuclear Safety Commission?
Are these not the concerns that should trigger a comprehensive
environmental review?
CNSC staff seems to be acting almost as an apologist for the
proponent, running interference for them by blocking efforts
to ensure a more thorough level of public accountability on
environmental matters. CCNR wonders what real value there
is in even having a regulatory agency if that is as far as it is
willing to go in terms of transparency, accountability, and
vigilance.
Thank you for considering these comments.
On behalf of the CCNR Board of Directors,
Yours very truly,
Gordon Edwards, Ph.D., President,
Canadian Coalition for Nuclear Responsibility.
References:
- AECL. Conceptual Decommissioning Plan for the Point LePreau GS, CANDU Operations, June 1987
- Edwards, Gordon. Estimating Lung Cancers, CCNR, 1978.
- Goodhead, Dudley et al. Report of the Committee Examining Radiation Risks of Internal Emitters (CERRIE), 2004.
- Thoms, Duncan and K. G. MacNeill. Risk Estimates for the Health Effects of Alpha Radiation, AECB, 1982.
- TLG Services Inc. Preliminary Decommissioning Plan for the Gentilly 2 Generating Station, Document No. H08-1374-003, Rev. 0, 2001.
- Woollard, R. and Eric Young. Health Dangers of Uranium Mining, BCMA (British Columbia Medical Association), 1980.
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