Going the Distance? the Safe Transport of Spent Nuclear Fuel and High-Level Radioactive Waste in the United States

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Going the Distance? the Safe Transport of Spent Nuclear Fuel and High-Level Radioactive Waste in the United States Going the Distance? The Safe Transport of Spent Nuclear Fuel and High-Level Radioactive Waste in the United States There are no fundamental technical barriers to the safe transport of spent nuclear fuel and high-level radioactive waste in the United States. When conducted in strict adherence to existing regulations, such transport is a low radiological risk activity with manageable safety, health, and environmental consequences. However, there are a number of social and institu- tional challenges to the successful initial implementation of large-quantity shipping programs. bout 55,000 metric tons of spent nuclear fuel and high-level radioactive waste— byproducts of nuclear power production, defense-related activities, and research Aactivities—are stored at more than 70 sites around the United States (see Figure 1). The vast majority is commercial spent fuel stored at nuclear power plant sites. The remainder is defense-related spent fuel and high-level waste stored at four government-owned sites. These materials are highly radioactive and, without proper shielding, can be harmful or fatal to those exposed to it. All of the U.S. sites are considered interim storage solutions. The federal plan is to transport spent fuel and high level waste from those sites to permanent disposal in a geologic repository that is to be built at Yucca Mountain, Nevada. The U.S. Department of Energy (DOE) is responsible for transporting spent fuel and high-level waste to the repository. Transportation of spent fuel on our nation’s railways and highways is nothing new. Since the 1950s, it has been transported in small quantities from a variety of sources, including nuclear-pow- ered naval ships, research facilities, and nuclear power plant sites that have been shut down or run short of storage. It is also being transported in many other countries, in some cases in much larger quantities than in the United States. To date, only about 3,000 metric tons of the total U.S. inventory has been transported, and that inventory is growing by about 2,000 metric tons per year. Figure 1. Locations Hanford WA Site of current spent fuel ME ND Idaho National West Valley and high-level waste Laboratory MN OR MT Demonstration VT storage sites, Yucca WI Project NY NH ID SD MA WY MI Mountain, and Private RI NJ Private Fuel IA PA CT Storage NE Fuel Storage. The stars NV OH MD DE Yucca UT IN are nuclear power plant Moutain CO IL WV KS VA sites; circles are govern- CA MO KY NC ment-owned sites for TN AZ OK NM AR defense-related wastes. SC MS AL GA Savannah Source: Modified from LA River Site the U.S. Department of TX Energy FL 1-1 TOP (left hand page) Landscape view With the potential opening of Yucca Mountain also includes social risks that arise from social pro- now estimated at 2017, attention has turned to the ques- cesses and people’s perceptions even in the absence tion of how to safely transport much larger quantities of of radiation exposures. Risks can also arise from spent fuel and high-level waste in the future. A large- incidents such as terrorist attacks, but such incidents scale transportation program is especially challenging are not addressed in this report. because much of the U.S. commercial spent fuel inven- tory is now being stored at sites near large populations, Health and Safety Risks of Transport Are and shipments would pass through 31 states and many Generally Low major population centers on their way to the repository. Recognizing the need for an independent ex- There are two potential sources of radiation amination of the risks and key concerns associated exposure during transport of spent fuel and high-level with this transport, the National Research Council’s waste: 1) emitted radiation or “radiation shine” from Nuclear and Radiation Studies Board and Transporta- packages during routine transport conditions; and 2) tion Research Board jointly initiated this study. A key potential increases in radiation shine and release of finding of the study report is that transport by highway radioactive materials under accident conditions severe (for small-quantity shipments) and by rail (for large- enough to compromise the robust containers or “pack- quantity shipments) is, from a technical viewpoint, ages” used to transport the spent fuel and high-level a low radiological risk activity with manageable waste. The report finds that the radiological risks safety, health, and environmental consequences when associated with the transportation of spent fuel and conducted in strict adherence to existing regulations. high-level waste are well understood and are generally However, there are a number of social and institu- low. This statement is based on several factors (de- tional challenges to the successful initial implementa- scribed in chapters 2 and 3 of the report) that include tion of large-quantity shipping programs that require the following: expeditious resolution as described in the report. • Rigorous international standards and U.S. regu- Moreover, the challenges of sustained implementation lations for the design, construction, testing, and should not be underestimated. maintenance of spent fuel packages; Assessing Transportation Risks • Full-scale crash testing of transport packages under severe accident conditions; Risk is a multidimensional concept: It in- cludes the health and safety risks that potentially arise • A series of increasingly sophisticated analytical from exposures of workers and members of the public and computer modeling studies of spent fuel to radiation from spent fuel and high-level waste. It transport package performance; and Limit or Dose (mSv) • Reconstructions of the mechanical 0.0001 0.001 0.01 0.1 1 10 100 and thermal loading conditions from DOE annual occupational dose limit 50 severe accidents that did not involve ICRP annual occupational dose limit 20 spent fuel to assess how spent fuel Current DOE annual occupational administrative limit 20 Max. dose to YM transportation worker (annual) 20 packages would have performed Single whole-body CT scan 12 under the same conditions. Annual natural background dose, South Dakota 9.6 YM post-10,000 year proposed dose limit (annual) 3.5 Annual natural background dose, U.S. average 3.0 However, extreme accidents Annual natural background dose, Florida 1.3 involving very-long-duration (hours ICRP annual public dose limit 1.0 to days) fires that fully engulf the Max. exposed YM SS worker, mostly truck (annual) 1.0 Single X-ray of human hip 0.6 transportation package might compro- Land disposal facility dose limit (annual) 0.25 mise its ability to contain its radioac- YM pre-10,000 year dose limit (annual) 0.15 Single roundtrip airline flight, New York -Tokyo 0.145 tive contents. While the likelihood of Max. exposed resident near YM rail stop (annual) 0.12 Exposure Examples such extreme accidents appears to be Single chest X-ray 0.1 very small, their occurrence cannot Max. hourly dose at 2 meters from trans. vehicle 0.1 Single X-ray of human extremity 0.01 be ruled out based on historical data Single round-trip airline flight, St. Louis-Tampa 0.009 Max. exposed resident along YM rail route (annual) 0.0007 for other types of hazardous materials shipments. However, the likelihood Figure 2. Estimates of radiation exposureLandscape from transport view of spent fuel and of occurrence and consequences can high-level waste under routine conditions. be reduced further through relatively Limit or Dose (mSv) 0.0001 0.001 0.01 0.1 1 10 100 DOE annual occupational dose limit 50 ICRP annual occupational dose limit 20 Current DOE annual occupational administrative limit 20 Max. dose to YM transportation worker (annual) 20 Single whole-body CT scan 12 Annual natural background dose, South Dakota 9.6 YM post-10,000 year proposed dose limit (annual) 3.5 Annual natural background dose, U.S. average 3.0 Annual natural background dose, Florida 1.3 ICRP annual public dose limit 1.0 Max. exposed YM SS worker, mostly truck (annual) 1.0 Single X-ray of human hip 0.6 Land disposal facility dose limit (annual) 0.25 YM pre-10,000 year dose limit (annual) 0.15 Exposure Examples Single roundtrip airline flight, New York -Tokyo 0.145 Max. exposed resident near YM rail stop (annual) 0.12 Single chest X-ray 0.1 Max. hourly dose at 2 meters from trans. vehicle 0.1 Single X-ray of human extremity 0.01 Single round-trip airline flight, St. Louis-Tampa 0.009 Max. exposed resident along YM rail route (annual) 0.0007 Portrait view fig 3-3 Please choose which view simple operational steps and route-specific analyses. Department of Energy for gathering information about The report recommends that transportation planners social risks in its Yucca Mountain transport program: and managers undertake detailed surveys of transpor- tation routes to identify potential hazards that could 1. Expand the membership and scope of an exist- lead to or exacerbate extreme accidents involving long ing advisory group to obtain outside advice on duration, fully engulfing fires, and also take steps to social risks, and avoid or mitigate such hazards. The report also recom- 2. Establish a transportation risk advisory group mends that the Nuclear Regulatory Commission build that is explicitly designed to provide advice on on recent progress in understanding package perfor- characterizing, communicating, and mitigating mance in very long duration fires through additional the social, security, and health and safety risks analyses. that arise from the transport of spent fuel. Potential for Harmful Radiation Exposure Low Although these recommendation are focused primarily on the Department of Energy, they apply to Transportation packages contain heavy shield- any large-quantity shipping program, including the ing to protect workers and the public from the radia- program to ship commercial spent fuel to centralized tion emitted by the spent fuel or high-level waste interim storage (e.g., Private Fuel Storage, LLC in contained within them.
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