Odpady jądrowe – globalny raport Focus Europe

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WNWR 2019  — 6. COSTS AND FINANCING

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the utilities set aside provisions for interim storage of their waste; the estimated discounted costs were around €5.8 billion in 2014.276 After the financing reform, this amount was transferred to an external segregated fund and all interim storage costs, including for spent nuclear fuel that will arise from continued operation, will be paid by the public fund. In Sweden, the costs for the centralized interim storage facility CLAB are paid by the Nuclear Waste Fund. The most complex financing situation for interim storage of spent nuclear fuel is in the US. The Nuclear Waste Policy Act required the Department of Energy (DOE) to take over spent nuclear fuel in 1998. This created a significant liability for the DOE. The absence of a high-level waste repository forces local utilities to store spent fuel on their own sites, including already decommissioned sites. For this interim storage, the utilities request substantial financial compensation from the DOE, which has spent over US$10 billion in legal penalties so far. DOE estimates that total damages could amount to US$20.8 billion, if it begins accepting fuel in 2020. With further delays, the liabilities could increase by hundreds of millions of dollars annually.277 The US Department of Justice manages a Judgment Fund of taxpayer money, about US$2 million per day, on all nuclear power plants, operating or shut down, to help manage their spent nuclear fuel. In France, EDF estimates an additional €18.7 billion (US$21.1 billion) for spent fuel management (for example storage, reprocessing), and another €1.2 billion (US$1.4 billion) for waste removal and conditioning.278 This amounts to €51 billion (US$57.5 billion) only for handling and storing the waste generated from operation. FINANCING SCHEMES FOR DISPOSAL The polluters are not always financially liable for disposal (and partly waste management, too); in some cases, liability is transferred to a state-governed organization that is also responsible for radioactive waste.279 Most countries require funds for the long-term management of radioactive waste to be managed externally and segregated from the operator or licensee. In France, for instance, the operators of nuclear power plants must bear all costs related to waste management, but an external fund for the construction and operation, final closure, maintenance, and monitoring of the intermediate- and high-level waste disposal installations was created. ANDRA, the state-owned waste management agency, holds and manages the fund (Article 16 of the 2006 Waste Law).280 In addition, there is also an internal, restricted ANDRA fund for research for future storage facilities. The two funds are fed by payments from the operator’s internal funds at the time they are needed. However, the only fund fed right now is the research fund, as there is still no construction license. Instead, the operators make payments from their internal fund (for waste management) to ANDRA’s general budget to finance operations related to the storage facilities for short-lived, medium-level waste.281 Due to the 2006 Waste Law, the assets in the funds of EDF and Areva have to be reported separately, and the market value has to be at least as high as the liabilities to be covered. If EDF goes bankrupt, the state can claim right over the assets. An administrative authority supervises the internal funds; it can impose corrective measures, including the right to impose payments to ANDRA’s budget. 276 Warth & Klein Grant Thornton AG Wirtschaftsprüfungsgesellschaft, 2015. 277 US Department of Energy 2012, “Blue Ribbon Commission on America’s nuclear future”. 278 EDF 2019, “Consolidated Financial Statements at 31 December 2018”. 279 Wuppertal Institut 2007. 280 Government of France 2006, The 2006 programme act on the sustainable management of radioactive materials and wastes,

Office parlementaire — Assemblée nationale. 281 Wealer, Hirschhausen, and Seidel 2019.


Articles inside

Quantities of waste

2hr
pages 97-148

Summary

1min
page 94

Costs and financing

2min
page 93

Waste management policies and facilities

2min
page 92

Financing schemes for interim storage

2min
page 84

Integrated financing schemes

2min
page 87

6.4 Summary

5min
pages 88-89

Financing schemes for disposal

6min
pages 85-86

Quantities of waste

2min
page 91

Decommissioning costs

6min
pages 80-81

Accumulation of the funds

3min
page 78

Overview and nature of the funds

2min
page 77

5.5 Summary

2min
page 75

Extended storage

4min
pages 73-74

Deep borehole disposal

3min
page 70

LILW-repositories

3min
page 67

Host rocks

2min
page 66

5.1 Historical background

16min
pages 58-62

5.2 The context of nuclear waste management

5min
pages 63-64

4.7 Summary

2min
page 57

4.5 Risks from the reprocessing of spent nuclear fuel

5min
pages 53-54

Risks to nuclear workers

3min
page 51

Uranium mine tailings

3min
page 49

Health risks from exposures to uranium

3min
page 47

4.1 Radiation risks of nuclear waste

2min
page 45

Uranium mining

3min
page 48

4.2 Risks from uranium mining, mine tailings, enrichment, and fuel fabrication

2min
page 46

3.4 Summary

4min
pages 43-44

Decommissioning waste

2min
page 34

Uranium mining, milling, processing and fuel fabrication

1min
page 22

Executive summary

28min
pages 11-20

Operational waste

2min
page 32

2.4 Summary

2min
page 30

2.3.1 The IAEA classification

5min
pages 25-26

2.1 Types of waste: the nuclear fuel chain

2min
page 21

Foreword

5min
pages 3-4

Key Insights

2min
pages 9-10
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