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WNWR 2019  —  5. WASTE MANAGEMENT CONCEPTS

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HOST ROCKS As the historical analysis shows, today’s repository concepts have developed relatively specifically in the direction of the disposal of nuclear waste in the continental crust (see chapter 5.1). From the very beginning, mainly salt rocks but also montmorillonites, such as clay minerals and clays, were regarded as particularly interesting host rocks due to their very low permeability and high sorption capacity. The search for siting areas for high-level waste focused particularly on these two types of rock. However, the options had to be extended relatively quickly to other host rocks because some countries did not have such formations in their subsoil. Especially the choice of crystalline rocks of the Baltic Shield by the two Nordic states using nuclear power (Sweden, Finland) is due to this circumstance. However, the Nordic programs in particular were forced to massively reinforce the artificial barriers (copper canisters) at the expense of geological isolation in order to counter the groundwater inflows through the fissured and permeable crystalline rock. Japan, too, resorted to the rocks found in the subsoil of the circum pacific fire belt: crystalline rocks and pelagic or hemipelagic sediments.190 There are also other exotics among the host rocks: volcanic tuffs, which were intended for example primarily for Yucca Mountain, Nevada191—the site of the US repository program that has been abandoned in the meantime (see section 7.8)—and which raise fundamental questions of suitability because of their permeability. Equally problematic are the generally relatively thin layers of anhydrite, which appear as rocks accompanying rock salt deposits. They were an early specialty of the Swiss disposal programs.192 Other rocks selected in the course of the site search were, for example, basalts in the US Hanford Program lying below the quaternary cover 193 or alpine marls of Wellenberg in Switzerland.194 Historically, “exotic” host rocks often occurred in the immediate vicinity of nuclear facilities or mines such as the iron ore mine of Schacht Konrad near Salzgitter in Germany 195 or the uranium mine “Beta” in the pegmatites of El Cabril in Spain.196 Regardless of the fact that only limited experience is available in the implementation of geological repositories, salt and clay rocks or crystalline rocks are usually considered to be particularly suitable host rock formations. 190 NEA 2016, Japan’s Siting Process for the Geological Disposal of High-Level Radioactive Waste, Nuclear Energy

Agency / OECD, viewed 1 August 2019, pp. 15, https://www.meti.go.jp/shingikai/enecho/denryoku_gas/genshiryoku/ chiso_shobun/pdf/018_s01_00.pdf 191 Walker, S. 2009, The Road to Yucca Mountain, University of California Press 192 Buser, M. 2017b, Short‐term und Long‐term Governance als Spannungsfeld bei der Entsorgung chemo‐toxischer Abfälle (Short-term and long-term governance as a field of tension in the disposal of chemotoxic waste), Vergleichende Fallstudie zu Entsorgungsprojekten in der Schweiz und Frankreich: DMS St‐Ursanne und das Bergwerk Felsenau (beide Schweiz) und Stocamine (Frankreich), ITAS‐ENTRIA‐Arbeitsbericht 2017‐02, viewed 1 August 2019, http://www.itas.kit.edu/pub/v/2017/buse17a.pdf 193 Milnes 1985, pp. 154-155. 194 Mosar, J. 2010, Beurteilung der Tektonik im Standortgebiet Wellenberg (Kt. NW/OW) hinsichtlich eines Tiefenlagers für schwach- und mittelradioaktive Abfälle (Assessment of tectonics in the Wellenberg siting area (NW/OW) with regard to a deep geological repository for low- and intermediate-level radioactive waste), Sachplan geologische Tiefenlager, z. Hd. Baudirektion Nidwalden, pp. 4-6, viewed 1 August 2019, https://www.nw.ch/_docn/30814/gutachten_tektonik_prof._mosar.pdf 195 Physikalisch-Technische-Bundesanstalt Braunschweig 2012, Schachtanlage Konrad (Shaft Konrad), viewed 1 August 2019, https://epic.awi.de/id/eprint/37594/1/schacht-konrad.pdf 196 Hernando-Fernández, J. L., Hernando Luna, R. 2002, Descubrimiento, explotación y tratamiento de los minerales radioactivos de Sierra Albarrana, El Cabril, Córdoba (Discovery, exploitation and treatment of the radioactive minerals of Sierra Albarrana), viewed 1 August 2019, https://helvia.uco.es/xmlui/bitstream/handle/10396/6947/braco143_2002_1.pdf?sequence=1&isAllowed=y


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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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