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Page 91

WNWR 2019  — 7. COUNTRY STUDIES

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intermediate-level waste (ILW) that contains a significant amount of long-lived radionuclides and thus requires a higher degree of isolation from the surrounding environment than low-level waste; and

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high-level waste (HLW), whose heat generated by the decay of the radionuclides it contains must be taken into account during its storage and disposal; after this waste is processed and treated, it must meet waste acceptance criteria and be disposed of in deep geological repositories several hundred meters underground.

QUANTITIES OF WASTE The Czech Republic has the largest volumes of nuclear waste of any of the more recent member states in the EU. In communist times, spent nuclear fuel was returned to the supplier, the Soviet Union. Since the early 1990s, however, Russia has no longer accepted returned nuclear waste. ČEZ, the operator of the Czech nuclear power plants, built dry cask storage facilities at its plants to store spent fuel after it had been removed from the spent fuel pool. There are two dry storage facilities the Dukovany plant and one at Temelín with a total capacity of 3,310 tons of spent fuel. The Czech government regularly publishes a waste inventory. The data below comes from the most recent inventory, which records waste volumes and activity as of December 31, 2016. TABLE 9: Nuclear waste in the Czech Republic as of December 31, 2016 Type of waste

SNF (HLW)

LILW LIQUID

LILW SOLID

Type of storage

Storage site

Quantity

Interim storage (dry)

Dukovany and Temelín

1,174 tHM

Interim storage (wet)

Dukovany and Temelín

654 tHM

Reactor storage tanks

Dukovany and Temelín

1,439 m³

Reactor storage facility

Dukovany and Temelín

351,3 t

Near-Surface repository (disposed)

Dukovany

11,520 m³

VLLW

n.a.

Source: Czech State Office for Nuclear Safety report to EURATOM 2018

Low- and intermediate-level waste produced by nuclear plants and research reactors is mostly treated on site; liquid waste is either bituminized or polymerized, whereas solid waste is either compacted or first incinerated before being compacted into 200 liter canisters. Intermediate-level waste unsuitable for deposition now is stored and will be deposited in the deep geological depository. The government estimates that after 40 years of operation of the Dukovany and Temelín plants nearly 3,500 tons of spent fuel would be produced.293 Every additional year of operation would produce another 35 tons of waste from Dukovany and 36 from Temelín. If three additional reactors were built, nearly 10,000 tons of spent fuel would need to be disposed of by mid-22nd century. In addition to spent fuel, this repository would also need to hold 4,200 tons of waste from decommissioned nuclear plants, 140 tons of operating waste, and 84 tons of other waste. 293 Government of the Czech Republic 2017, “Policy for Spent Nuclear Fuel and Radioactive Waste Management in the Czech

Republic”, 29 November, viewed 29 May 2019, https://www.mpo.cz/assets/cz/energetika/strategicke-a-koncepcni dokumenty/2017/12/Koncepce-nakladani-s-RaO-a-VJP-v-CR.pdf


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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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