Odpady jądrowe – globalny raport Focus Europe

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WNWR 2019  — 3. QUANTITIES OF WASTE

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All these processes produce nuclear waste. The first waste that emerges is the tailings (excavated rocks to access the uranium ore) at the mine. In some cases, these tailings were stockpiled in heaps to fill open-cast mines or to redevelop areas. Six countries supply around 85 percent of the world’s mined uranium: Canada, Kazakhstan, Australia, Niger, Namibia, and Russia.22 Mining (and subsequent processes) creates large amounts of nuclear waste in the exporting countries, of which only Canada and Russia operate nuclear power plants. France, Russia, Canada, China, and the US commercially convert yellow cake into uranium hexafluoride (UF6). England, France, Germany, the Netherlands, Russia, Japan, and the US provide commercial enrichment services. Uranium-containing waste is generated in both stages. OPERATIONAL WASTE The operation of nuclear power plants for electricity generation produces different kinds of nuclear waste in different kinds of physical states, of which the lion’s share is low- and intermediate-level waste (LILW). The IAEA classifies operational waste into two main categories: unconditioned (as-generated) and conditioned operational waste. For unconditioned operational waste, an indication of the physical state (such as liquid or solid) is important:23 ••

Raw waste (waste in its original form) is unconditioned and often listed in tons for solid waste and cubic meters (m³) for liquid waste.24

••

But this category also includes pre-treated waste. This waste has undergone some form of preconditioning and is often measured in tons for solids and m³ for liquids.

To bring the waste into a stable and immobilized form and to make it suitable for transportation, storage, and eventually disposal, it needs to be conditioned. Waste compaction is also applied in order to minimize the waste quantities; compaction can be a part of conditioning but does not have to be.25 ••

An additional category is conditioned waste that has to be reconditioned for safety or acceptance reasons or both.26

••

After conditioning, the waste is stored in drums, storage, transport, or disposal casks. The stored waste is measured in m³, metric tons, or number of casks or drums.

••

A last waste category is disposed waste. In Europe, only less than half of the nuclear countries have installed disposal facilities for LILW (UK, France, Spain, Hungary, Finland, Czech Republic, Sweden). Disposed waste is often measured in m³ or waste packages or casks.

22 Mendelevitch, R., Dang, T. 2016, “Nuclear Power and the Uranium Market: Are Reserves and Resources Sufficient?”,

DIW Berlin — Deutsches Institut für Wirtschaftsforschung. 23 Solid waste is for example protective clothing, replaced plant components, or insulation material. Liquid waste is for

example cooling water contamination, oils, vaporizer concentrates, filter substances, or sludge, which forms when solid matter collects as sediment at the bottom of pumps. See IAEA, “Categorizing Operational Radioactive Wastes”, International Atomic Energy Agency, 2007. 24 Or mega gram (Mg) of heavy metal (HM). 25 For more details on the waste production techniques, see Homberg, Pavageau, and Schneider 1997 “Cogema — La Hague The Waste Production Techniques”, Greenpeace International. 26 For example, bituminized sludges from reprocessing that AREVA client countries refuse to take back and that turn out sub-spec for final disposal in France.


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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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