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Under
the Nuclear Waste Policy Act of 1982 (Text),
spent fuel must be disposed of in a geologic repository and under
the terms of NWPA Amendments of 1987, Yucca Mountain, Nevada is
the only site under study for the repository. The Energy Policy
Act of 1992 (Text)
required that the NRC modify its licensing criteria for disposal
of spent nuclear fuel and high-level radioactive wastes in the proposed
geologic repository at Yucca Mountain, Nevada to be consistent with
the Environmental Protection Agency's final site-specific standard
for Yucca Mountain. The NRC published its final licensing criteria,
known as 10 CFR 63 (Text)
on November 2, 2001. Part 60 of the Code of Federal Regulations
(CFR) (Text)
governs disposal of high-level radioactive waste in geologic repositories.
According
to the DOE Total Life Cycle Cost Report for the Yucca Mountain site,
DOE has already spent $6.7 billion on the repository program, and
estimates that approximately $50 billion will be spent during the
lifetime of the Yucca Mountain project. The NWPA established the
Nuclear Waste Fund (the Fund) to pay for the costs of characterizing
and developing a permanent repository. The Fund is derived from
fees collected from a 1.0 mil per kilowatt-hour assessment on all
electricity generated by commercial nuclear power plants, as well
as equivalent assessments on quantities of spent fuel or other high
level wastes to be disposed of at Yucca Mountain from Federal agencies.
In return, the Secretary is required to accept title, subsequently
transport, and dispose of a generator's spent fuel and high-level
wastes. The NWPA required the Secretary to begin disposal of these
wastes not later than January 31, 1998. The U.S. Government has
signed contracts with nuclear power producers agreeing to take their
spent fuel, and setting up a timetable and regulations regarding
shipments. (Text
of Contract) For every delay in opening the repository, and
every timeline not met by the Department of Energy, the industry
is racking up charges against the U.S. taxpayer. (Story)
TRU
waste is to be disposed of in a repository specifically built for
TRU located at the Waste Isolation Pilot Plant, or WIPP, at Carlsbad,
New Mexico.
In
order to bury the waste in these repositories it must be transported
from where it is now (Map),
to their locations, so first we will discuss transportation issues.
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| Transportation
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All
spent nuclear fuel and high-level radioactive waste destined for
the repository will be in solid form. These materials would be transported
to a repository in large, strong containers called casks on trains,
barges, and trucks. Requirements for Radioactive Material Packages
in the storage and transportation of radioactive material are determined
by the Nuclear Regulatory Commission (NRC), Department of Transportation
(DOT), Department of Energy (DOE), and U.S. Postal Service (USPS).
There are, of course, strict regulations governing the shipment
and packaging of radioactive materials as there are for hazardous
materials. We all know how carefully trucking companies follow the
rules, but in this case although there have been the usual leaking,
damaged and mishandled packages, no one has actually been seriously
injured by a shipment of nuclear materials. The industry’s safety
record is pretty good, better than shippers of hazardous materials,
who have been involved in 99,490 incidents resulting in 356 major
injuries, 114 deaths, and $317,523,997 in damages between January
7, 1987 and December 31, 1996. Since 1965, more than 2,500 shipments
of spent nuclear fuel have been safely carried out in the United
States between nuclear power plants, government research facilities,
and industrial complexes.
In
the early 1980's, DOE leased capsules containing radioactive cesium-137
to commercial irradiation facilities to sterilize medical equipment.
In 1990, a single capsule leaked at one of the commercial facilities
in Decatur, Georgia. DOE decided to recall all cesium capsules from
commercial operators and transport them to their place of origin,
the Waste Encapsulation and Storage Facility in Hanford, Washington.
Though the cesium capsules, in the form of cesium chloride salt,
are small (21 inches long, 6 inches in diameter, and weighing about
20 pounds), they are highly radioactive and must be stored under
water and handled remotely with heavy shielding during use and transportation.
DOE
and states along the cesium transportation routes worked together
to develop stringent protocols and procedures to be followed during
the cesium return shipping campaign. Many of these procedures had
been developed in anticipation of WIPP shipments, including enhanced
inspection criteria developed in conjunction with the Commercial
Vehicle Safety Alliance (CVSA), use of a detailed transportation
plan, and use of a responsible carrier with well-trained, dedicated
drivers. The shipments were conducted over the course of one year
beginning in May 1994. The
shipping campaign was very successful with no incidents or accidents.
The
DOE estimates that 0.7-3.0 accidents will occur per million shipment
miles by truck and 11.9 accidents per million shipment miles by
train. The estimate of shipment miles in millions over the next
30 years is 62.3 by truck and 14.0 by rail, resulting in an estimate
of the number of accidents likely to occur of between 210-354. Accidents
are inevitable.
In September of 1977, the NRC issued a generic Environmental Impact
Statement (EIS), titled Final Environmental Statement on the
Transportation of Radioactive Material by Air and Other Modes,
NUREG-0170, that provided the regulatory basis for issuance of general
licenses for transportation of radioactive material under 10 CFR
71. The EIS covered the transport of all types of radioactive material
by all transport modes (road, rail, air, and water). NUREG-0170
estimated the radiation doses and latent cancer fatalities that
might be associated with the transportation of 25 different radioactive
materials by plane, truck, train, and ship or barge. One of the
25 radioactive materials examined by NUREG-0170 was spent power
reactor fuel. The estimates used in the EIS were made using Version
1 of the RADTRAN code (RADTRAN 1), that was developed specifically
to perform the NUREG-0170 study. RADTRAN is a computer program which
has become the standard for transportation risk assessment. The
code was developed at Sandia National Laboratories. RADTRAN combines
user-determined meteorological, demographic, transportation, packaging,
and material data with health physics data to calculate the expected
radiological consequences and accident risk of transporting radioactive
materials.
The
so-called Modal Study for the NRC, more properly titled "Shipping
Container Response to Severe Highway and Railway Accident Conditions"
NUREG/CR-4829, concluded that extremely few accidents would pose
a significant radiation hazard to the public, concurring with previous
NRC regulatory evaluations, namely NUREG-0170, that "indicate
that the expected radiological consequences from the shipment of
3000 metric tons of spent fuel per year is less than 1 latent cancer
fatality every 2300 years." Prepared
for NRC by Lawrence Livermore National Laboratory and authored by
Larry E. Fischer, et al. in 1987, the study has been criticised
by opponents of the nuclear industry for it's methods and assumptions.
(PDF 10M)
The State of Nevada has questioned the studies conclusions regarding
the safety of transporting Spent Nuclear Fuel to the proposed repository
saying that "the Modal Study is a good start, but it is too
simplistic, incomplete, outdated and open to serious question to
be used as the basis for any present-day environmental or risk assessment
of spent fuel transportation". The Modal Study itself was intended
to answer questions that remained from a previous study. Sandia
updated the Modal Study, with a new study referred to as Package
Performance Study (PPS) an "Update of Spent Fuel Shipping Container
Response to Severe Highway and Railway Accidents." (Website)
They reexamined the methods and conclusions of the original study
and went to lengths to attempt to address the concerns of it's critics.
NRC
U.S.-Specific Schedules of Requirements for Transport of Specified
Types of Radioactive Material Consignments (PDF
242K)
Examination
by the Congressional Research Service in May of 1998 of the prior
studies done by the NRC on the safety of transporting SNF, the methods
used in arriving at the conclusions stated by these studies and
the critics of the governments reports. The CRS prepared a report
entitled Transportation
of Spent Nuclear Fuel outlining the various points of view for
the benefit of Congress members.
When
the repository is ready to accept waste a huge increase in the number
of shipments is expected from the current total 2,400 to 104,500
through 43 states and within a half mile of 50 million Americans.
According to the industry group the Nuclear Energy Institute, of
the 100 million packages shipped each year in the U.S. containing
hazardous materials only 2% are radioactive materials and only 250,000
contain material resulting from the generation of nuclear power,
the rest are medical and industrial materials. NEI points to the
industry’s prior shipping experience of over 46 million packages
of radioactive materials shipped, of which 3,453 were involved in
accidents during the period since 1971.
The
group Public Citizen makes the point that all it takes is one accident
and describes the DOE’s study as part of the 1986 Environmental
Assessment which outlines a rural accident with a release of 1,380
Ci which they determined “would contaminate an area of 42 square
miles requiring 450 days and $620 million to clean up”. Since the
consequences of an accident are so significant, and considering
the inevitability of accidents in general, the NRC has placed a
great deal of importance on the packaging of radioactive materials.
The containers approved for use in shipping high level waste and
spent fuel have been designed to survive accidents intact, and packaging
for lower level material emphasizes sturdiness.
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Packaging
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A range
of packaging options is available depending upon the nature of the
material to be shipped. Beginning with the least restrictive type,
Excepted Packaging (EP) (Photo)
is used for very slightly radioactive material such as smoke detectors
or watch dials and generally consists of a fiberboard box or other
type of package chosen for ease of handling. Excepted Packagings
are designed to survive normal conditions of transport. Excepted
packagings are used for transportation of materials that are either
Low Specific Activity (LSA
Definition ) or Surface Contaminated Objects (SCO
Definition ) and that are limited quantity shipments, instruments
or articles, articles manufactured from natural or depleted uranium
or natural thorium; empty packagings are also excepted (49CFR 173.421-428).
(Definition) For more
specific information see NUREG 1608 (PDF
448K) NRCs "Categorizing and Transporting Low Specific Activity
Materials and Surface Contaminated Objects"
Industrial
Packagings (IP) (Photo) are used
for materials that present a limited risk such as contaminated equipment
or waste that has been solidified in a material such as concrete.
There are three classes of IP based upon strength. IP 1 must meet
design requirements of Excepted Packaging, IP 2 must pass free drop
and stacking tests, and IP 3 must also pass the water spray and
penetration tests required for Type A. Industrial Packingings (IP)
are designed to survive normal conditions of transport (ip-1) and
at least the DROP test and stacking test for Type A packingings
(IP-2 and IP-3). Industrial packingings (IP) are used for transportation
of materials with very small amounts of radioacitivity such as Low
Specific Activity [LSA] or Surface Contaminated Objects [SCO] (Definitions).
Industrial packingings (IP) are usually metal boxes or drums.
Type
A Packagings (Photo) are used
for materials such as radiopharmaceuticals and low level waste and
have integral shielding and are designed to protect and retain their
contents. There is an inner containment vessel of glass, plastic
or metal and packaging material of polyethylene, rubber, or an absorbent
such as vermiculite. Type A Packagings are designed to survive normal
transportation, handling, and minor accidents. A minor accident
is defined as "An accident that does not subject the radioactive
material package to conditions that are more severe than those typically
associated with transportation. A Type A package would not release
its radioactive material contents if it was on a conveyance that
was involved in a minor accident". They are used for the transportation
of limited quantities of radioactive material (RAM) that would not
result in significant health effects if they were released. Type
B packagings are certified as Type A on the basis of performance
requirements, which means it must survive certain tests. Type A
packagings may be cardboard boxes, wooden crates, or drums. The
shipper and carrier must have documentation of the certification
of the packages being transported. (Definitions)
Type
B Packagings (Photo) vary
from 55 gallon drums to spent fuel casks. They are heavily shielded
and are used to transport spent fuel, HLW, cobalt and cesium sources.
Type B Packagings must be able to survive severe accidents. They
are used for the transportation of large quantities of radioactive
material. A Type B packaging may be a metal drum or a huge, massive
shielded transport container. Type B packagings must meet severe
accident performance standards that are considerably more rigorous
than those required for Type A packages. Type B packagings either
have a Certificate Of Compliance (COC)1
by the Nuclear Regulatory Commission (NRC) or Certificate
of Competent Authority (COCA)2
by the Department of Transportation
(DOT). (Definitions)
Strong
Tight Packaging (Example)
is used only for domestic shipment of low level material in a truck
reserved for this purpose. Materials such as natural uranium or
decommissioning rubble may use Strong Tight Packagings. The packages
may consist of wood or metal boxes, steel drums, or bins. Large
quantities of slightly contaminated rubble may be hauled in dump
trucks
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Regulatory
Oversight |
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Rules
for shipment of radioactive material are made by the U.S. Department
of Transportation and the NRC under Title 49 and Title 10 of the
Code of Federal Regulations respectively. Additional regulatory
oversight comes from the U.S. Postal Service, OSHA and the EPA.
Shipments of Special Nuclear Materials are also covered under the
International Convention on the Physical Protection of Nuclear Material
signed at Vienna and New York on March, 3, 1980 to which the United
States is a signatory. The Convention seeks to prevent sabotage,
hijacking, theft, or diversion to prevent nuclear proliferation
by setting standards to which the signatories and parties agree
to abide. 108 nations are signatories or parties to the agreement.
The Convention defines the nuclear materials it covers as Pu, U235,
U233, and Irradiated Fuel and specifically recommends
a number of measures to protect such material while it is in transit.
These include limiting the time spent in transit, minimizing transfers,
avoiding regular scheduling of shipments, security checks of those
providing protection to the transport including armed guards, careful
selection of route, continuous two way radio communication and search
of vehicle prior to loading to detect sabotage devices. NUREG
1660, (PDF file. 241K) describes NRCs U.S.-Specific Schedules
of Requirements for Transport of Specified Types of Radioactive
Material Consignments.
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Labeling
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In
addition to packaging, the shipment of nuclear material requires
appropriate marking, labeling and placarding of the individual containers
and of the vehicle. The markings must provide the shipping name,
identification number and shippers name and address. Labels index
the hazard level of the material using one of three diamond shaped
labels, Radioactive White I, Yellow II, or Yellow III. The label
provides information about the contents and its handling. The Contents
line identifies the contents, the Activity line gives the level
of radioactivity in curies, and on Yellow II and III the Transport
index states how many containers may be shipped together which is
based upon the level of radiation 1 meter from the containers. (Definitions)
Vehicles transporting certain types of materials must be marked
with placards designed to identify their contents to first responders
on all four sides of the vehicle. These are the same type of diamond
shape placard placed on all hazardous cargo. Shipments of high level
activity such as spent fuel are identified as High Route Controlled
Quantity and must have a white square behind the placard and must
use identified bypasses avoiding city centers were posted. This
is termed preferred routing and restricts transport based on a variety
of factors such as accident rate, population density, etc. A preferred
route is an Interstate Highway or other route designated by the
Department of Transportation. The entire route is mapped out in
advance and written instructions and maps are given to the driver.
It is the responsibility of the shipper to adhere to all regulations
governing transportation of nuclear material.
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Safety
Tests and Transportation Safety |
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The
Department of Transportation has conducted a series of rather spectacular
looking tests of transport casks, they have a video available that
shows them burning casks in pools of aviation fuel, dropping them
from 30 feet onto a hard surface, attempting to impale them on spikes
and submerging them in 50 feet of water. (Illustration)
Testing is done with both scale model and full size casks as well
as computer simulations. They developed specifications for the casks,
private industry built the models based upon these specifications
and then DOT tests them. Each design that passes the tests, real
or simulated, receives certification from the NRC. Shippers are
required to use certified model casks. The NRC has certified a variety
of casks for various purposes. The TN 8L by Transnuclear Inc., Certification
Number USA/9015/B( )F can carry three PWR assemblies for transport
by truck. It is stainless steel with lead, steel and resin shielding,
18 ½ feet long by 5 ½ feet in diameter and weighs 79,380 pounds
empty. A similar model, the TN 9 is available for shipping seven
BWR assemblies. They are classed as overweight truck casks for highway
use. There are currently four casks available and they are used
30-50 times per year.
The
NAC-LWT by NAC International, certification number USA/9225/B( )F
can carry one PWR assembly or two BWR assemblies by truck. It is
steel cased and lead shielded, 16 ½ feet long by 3 ½ feet in diameter
and weighs 51,200 pounds loaded. It is classed as a legal weight
truck cask. There are currently five casks available and they are
used 30-50 times per year. The NL1-1/2 by NAC International, certification
number USA/9010/B( )F can carry two BWR assemblies or one PWR assembly
by truck. It is steel encased with lead and depleted uranium shielding,
16 ¼ feet long by 3 ¾ feet in diameter and weighs 49,250 pounds
loaded. It is classed as a legal weight truck cask. There are currently
five casks available and they are used 30-50 times per year. The
IF-300 by General Electric, certification number 9001, can carry
7 PWR assemblies or 18 BWR assemblies by train. This 70 ton rail
cask is 17 feet long by 5 ¼ feet in diameter and weighs 140,000
pounds when loaded. It is stainless steel encased, shielded by depleted
uranium, stainless steel and water ethylene glycol solution. There
are currently four casks available and they are used two times a
month. The NAC-STC by NAC International can carry 26 PWR assemblies
or 57 BWR assemblies. Certified for both storage and rail transport,
it weighs 125 tons loaded. (Illustration)
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Transportation
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The
US Nuclear Waste Technical Review Board, an independent agency created
by Congress, points out that the current fleet of casks is sufficient
for only 100-200 metric tons of spent fuel per year when spent fuel
is being generated at the rate of 2,000 metric tons per year with
an existing backlog at reactors sites of 35,000 metric tons. They
note that before shipments to a repository could begin additional
casks of larger capacity must be designed, manufactured, tested
and certified. Several cask designs are in the process of being
approved. The Hi-Star 100 cask by Holtec International has a capacity
of 24 PWR or 68 BWR assemblies. It is designed to be used for storage
as well as rail shipping. Another dual purpose cask, the Vectra
MP-187 designed by Vectra Technologies will hold 24 PWR ASSEMBLIES.
The DOE was working on a cask to be a multi purpose cask, called
the MPC, which would be usable for storage, transportation and disposal.
The plan was to produce the cask as a generic cask that could be
used for repository disposal. There were to be two models, the smaller
MPC 75 and the larger MPC 125. MPC 75 would hold 12 PWR or 24 BWR
assemblies, MPC 125 would hold 21 PWR or 40 BWR assemblies. Westinghouse
Electric was the contractor to design and produce the cask, however,
at this point funding for the development of the MPC has been cut.
The two casks would have been used for rail transport as the MPC
75 weighed 75 tons and the MPC 125 weighed 125 tons. The NRC has
reviewed a high capacity truck cask by General Atomics, the GA4
and GA9 which would hold four PWR or nine BWR assemblies. The NRC
has issued a certificate of compliance to General Atomics of San
Diego, California, for
the GA-4 Legal Weight Truck Spent Fuel Shipping Cask, designed to
transport a variety of pressurized water reactor fuel types and
is classified as a Type B(U) package. It can transport up to four
irradiated spent fuel assemblies, each holding from 176 to 208 fuel
rods from 128 to 145 inches long. Designed primarily of stainless
steel, the cask is about 188 inches long and 40 inches in diameter.
Maximum weight with contents is 27.5 tons. Since this is a legal-weight
truck cask under Department of Transportation regulations, it would
be able to travel on any highway in the United States. Loaded rail
casks can weigh as much as 136 metric tons (150 tons); loaded truck
casks can weigh up to 23 metric tons (26 tons).
Under
the Nuclear Waste Policy Act of 1982, as amended, the DOE is required
to use only casks that are certified by the NRC for transporting
spent nuclear fuel and high-level radioactive waste to a repository.
To certify a cask, the NRC requires a design to withstand a series
of impact, puncture, and fire tests, thereby providing reasonable
assurance that packages will withstand serious transportation accidents.
1 A cask design must demonstrate that it can and will protect against
radiological release to the environment under the hypothetical accident
conditions consecutively posed in a 9-meter (30-foot) free-fall
on to an unyielding surface; a puncture test allowing the container
to free-fall 1 meter (40 inches) onto a steel rod 15 centimeters
(6 inches) in diameter; a 30-minute, all-engulfing fire at 800 degrees
Celsius (1475 degrees Fahrenheit); and immersion under 0.9 meter
(3 feet) of water. For casks designed to transport spent fuel, an
additional hypothetical accident condition is required in which
an undamaged package must be subjected to a one-hour immersion under
200 meters (655 feet) of water.
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