Deep geological repository
This article needs to be updated.September 2019)(
A deep geological repository is a way of storing toxic or radioactive waste within a stable geologic environment (typically 200–1000 m deep). It entails a combination of waste form, waste package, engineered seals and geology that is suited to provide a high level of long-term isolation and containment without future maintenance. A number of mercury, cyanide and arsenic waste repositories are operating worldwide including Canada (Giant Mine) and Germany (potash mines in Herfa-Neurode and Zielitz).
Principles and backgroundEdit
Highly toxic waste that cannot be further recycled must be stored in isolation to avoid contamination of air, ground and underground water. Deep geological repository is a type of long-term storage that isolates waste in geological structures that are expected to be stable for millions of years, with a number of natural and engineered barriers. Natural barriers include a water-impermeable (e.g. clay) and gas-impermeable (e.g. salt) layers of rock above and surrounding the underground storage. Engineered barriers include bentonite clay and cement.
The International Panel on Fissile Materials has said:
It is widely accepted that spent nuclear fuel and high-level reprocessing and plutonium wastes require well-designed storage for periods ranging from tens of thousands to a million years, to minimize releases of the contained radioactivity into the environment. Safeguards are also required to ensure that neither plutonium nor highly enriched uranium is diverted to weapon use. There is general agreement that placing spent nuclear fuel in repositories hundreds of meters below the surface would be safer than indefinite storage of spent fuel on the surface.
However, even a storage space hundreds of metres below the ground might not be able to withstand the pressures of one or more future glaciations with thick sheets of ice resting on top of the rock, deforming it and creating internal strains. This is being taken into consideration by agencies preparing for long-term waste repositories in Sweden, Finland, Canada and some other countries that would have to expect a renewed ice age. Natural uranium ore deposits serve as proof of concept for stability of radioactive elements in geological formations — Cigar Lake Mine for example is a natural deposit of highly concentrated uranium ore located under sandstone and quartz layer at depth of 450 m that is 1 billion years old with no radioactive leaks to the surface.
Common elements of repositories include the radioactive waste, the containers enclosing the waste, other engineered barriers or seals around the containers, the tunnels housing the containers, and the geologic makeup of the surrounding area.
The ability of natural geologic barriers to isolate radioactive waste is demonstrated by the natural nuclear fission reactors at Oklo, Gabon. During their long reaction period about 5.4 tonnes of fission products as well as 1.5 tonnes of plutonium together with other transuranic elements were generated in the uranium ore body. This plutonium and the other transuranics remained immobile until the present day, a span of almost 2 billion years. This is quite remarkable in view of the fact that ground water had ready access to the deposits and they were not in a chemically inert form, such as glass.
Despite a long-standing agreement among many experts that geological disposal can be safe, technologically feasible and environmentally sound, a large part of the general public in many countries remains skeptical as result of anti-nuclear campaigns and lack of knowledge. One of the challenges facing the supporters of these efforts is to demonstrate confidently that a repository will contain wastes for so long that any releases that might take place in the future will pose no significant health or environmental risk.
Nuclear reprocessing does not eliminate the need for a repository, but reduces the volume, the long-term radiation hazard, and long-term heat dissipation capacity needed. Reprocessing does not eliminate the political and community challenges to repository siting.
Deep geologic disposal has been studied for several decades, including laboratory tests, exploratory boreholes, and the construction and operation of underground research laboratories where large-scale in-situ tests are being conducted. Major underground test facilities are listed below.
|Belgium||HADES Underground Research Facility||Mol||plastic clay||223 m||in operation 1982|
|Canada||AECL Underground Research Laboratory||Pinawa||granite||420 m||1990–2006|
|Finland||Onkalo||Olkiluoto||granite||400 m||under construction|
|France||Meuse/Haute Marne Underground Research Laboratory||Bure||claystone||500 m||in operation 1999|
|Japan||Horonobe Underground Research Lab||Horonobe||sedimentary rock||500 m||under construction|
|Japan||Mizunami Underground Research Lab||Mizunami||granite||1000 m||under construction|
|South Korea||Korea Underground Research Tunnel||granite||80 m||in operation 2006|
|Sweden||Äspö Hard Rock Laboratory||Oskarshamn||granite||450 m||in operation 1995|
|Switzerland||Grimsel Test Site||Grimsel Pass||granite||450 m||in operation 1984|
|Switzerland||Mont Terri Rock Laboratory||Mont Terri||claystone||300 m||in operation 1996|
|United States||Yucca Mountain nuclear waste repository||Nevada||tuff, ignimbrite||50 m||1997–2008|
Nuclear repository sitesEdit
|Argentina||Sierra del Medio||Gastre||granite||Proposed 1976, stopped 1996|
|Belgium||Hades (High-activity disposal experimental site)||high-level waste||plastic clay||~225 m||under discussion|
|Canada||OPG DGR||Ontario||200,000 m3 L&ILW||argillaceous limestone||680 m||license application 2011|
|Canada||NWMO DGR||Ontario||spent fuel||siting|
|Finland||VLJ||Olkiluoto||L&ILW||tonalite||60–100 m||in operation 1992|
|Finland||Loviisa||L&ILW||granite||120 m||in operation 1998|
|Finland||Onkalo||Olkiluoto||spent fuel||granite||400 m||in operation|
|France||high-level waste||mudstone||~500 m||siting|
|Germany||Schacht Asse II||Lower Saxony||salt dome||750 m||closed 1995|
|Germany||Morsleben||Saxony-Anhalt||40,000 m3 L&ILW||salt dome||630 m||closed 1998|
|Germany||Gorleben||Lower Saxony||high-level waste||salt dome||proposed, on hold|
|Germany||Schacht Konrad||Lower Saxony||303,000 m3 L&ILW||sedimentary rock||800 m||under construction|
|Japan||Vitrified high-level waste||>300 m||under discussion|
|South Korea||Wolseong||Gyeongju||L&ILW||80 m||in operation 2015 |
|South Korea||high-level waste||siting |
|Sweden||SFR||Forsmark||63,000 m3 L&ILW||granite||50 m||in operation 1988|
|Sweden||Forsmark||spent fuel||granite||450 m||license application 2011|
|United Kingdom||high-level waste||under discussion|
|United States||Waste Isolation Pilot Plant||New Mexico||transuranic waste||salt bed||655 m||in operation 1999|
|United States||Yucca Mountain Project||Nevada||70,000 ton HLW||ignimbrite||200–300 m||proposed, canceled 2010|
The current situation at certain sitesEdit
The process of selecting appropriate deep final repositories is now under way in several countries with the first expected to be commissioned some time after 2010.
There was a proposal for an international high level waste repository in Australia and Russia. However, since the proposal for a global repository in Australia (which has never produced nuclear power, and has one research reactor) was raised, domestic political objections have been loud and sustained, making such a facility in Australia unlikely.
Giant Mine has been used as deep repository for storage of highly toxic arsenic waste in the form of powder. As of 2020 there is ongoing research to reprocess the waste into a frozen block form which is more chemically stable and prevents water contamination.
The Onkalo site in Finland is the furthest along the road to becoming operational, with waste burial currently scheduled to begin in 2020. Posiva started construction of the site in 2004. The Finnish government issued the company a licence for constructing the final disposal facility on 12 November 2015. As of June 2019[update] continuous delays mean that Posiva now expects operations to begin in 2023.
A number of repositories including potash mines in Herfa-Neurode and Zielitz have been already used for years for storage of highly toxic mercury, cyanide and arsenic waste. There is little debate in Germany regarding toxic waste in spite of the fact that unlike nuclear waste it does not lose toxicity with time.
There is a debate about the search for a final repository for radioactive waste, accompanied by protests, especially in the Gorleben village in the Wendland area, which was seen ideal for the final repository until 1990 because of its location in a remote, economically depressed corner of West Germany, next to the closed border to the former East Germany. After reunification, the village is now close to the center of the country, and is currently used for temporary storage of nuclear waste. The pit Asse II is a former salt mine in the mountain range of Asse in Lower Saxony/Germany, that was allegedly used as a research mine since 1965. Between 1967 and 1978 radioactive waste was placed in storage. Research indicated that brine contaminated with radioactive caesium-137, plutonium and strontium was leaking from the mine since 1988 but was not reported until June 2008 The repository for radioactive waste Morsleben is a deep geological repository for radioactive waste in the rock salt mine Bartensleben in Morsleben, in Saxony-Anhalt/Germany that was used from 1972–1998. Since 2003 480,000 m3 (630,000 cu yd) of salt-concrete has been pumped into the pit to temporarily stabilize the upper levels.
Sweden is working on plans for direct disposal of spent fuel using the KBS-3 technology. However the earliest approvals for construction can be given is 2021 and at the present time the earliest commercial operation could be scheduled to start is 2030.
The UK has been following the path towards geological disposal since the 2008 Defra White Paper, entitled "Managing Radioactive Waste Safely" (MRWS). Unlike other developed countries the UK has placed the principle of voluntarism ahead of geological suitability. When seeking local council volunteers for stage 1 of the MRWS process, only Allerdale and Copeland in Cumbria were volunteered by their councils. The same area that was previously examined and rejected in the 1990s. Stage 2 which was an initial unsuitability screening process, was carried out by British Geological Survey (BGS) in 2010. This ruled out approximately 25% of the land area based on the presence of certain minerals and aquifers. There remains some controversy about this stage following accusations that the criteria were changed between the draft and final versions of this report, bringing the Solway Plain back into consideration, however the criteria were clearly published in the 2008 Defra White Paper, entitled Managing Radioactive Waste Safely (MRWS) 2 years prior to being applied.
In June 2012, the independent geologist advising the local West Cumbria MRWS Partnership group named three rock volumes that could be potentially suitable for geological disposal of nuclear waste. These are the Mercia Mudstone Group rocks between Silloth, Abbeytown and Westnewton in North Cumbria, and the Ennerdale and Eskdale granites further south which lie within the Lake District National Park.
The decision on whether to proceed to the next stage was due to be taken in January 2013 by a group of seven councillors, forming the Executive of Allerdale and another seven from Copeland. The ten member cabinet of Cumbria County Council had a veto which would prevent the search continuing.
In January 2013, Cumbria county council used its veto power and rejected UK central government proposals to start work on a production reactor nuclear waste repository near the Lake District National Park. "For any host community, there will be a substantial community benefits package and worth hundreds of millions of pounds" said Ed Davey, Energy Secretary, but nonetheless, the local elected administrative and governing body voted 7–3 against research continuing, after hearing evidence from independent geologists that "the fractured strata of the county was impossible to entrust with such dangerous material and a hazard lasting millennia."
The Waste Isolation Pilot Plant (WIPP) in the United States went into service in 1999 by putting the first cubic metres of transuranic radioactive waste in a deep layer of salt near Carlsbad, New Mexico.
In 1978 The U.S. Department of Energy began studying Yucca Mountain, within the secure boundaries of the Nevada Test Site in Nye County, Nevada, to determine whether it would be suitable for a long-term geologic repository for spent nuclear fuel and high-level radioactive waste. This project faced significant opposition and suffered delays due to litigation by The Agency for Nuclear Projects for the State of Nevada (Nuclear Waste Project Office) and others. The Obama Administration rejected use of the site in the 2009 United States Federal Budget proposal, which eliminated all funding except that needed to answer inquiries from the Nuclear Regulatory Commission, "while the Administration devises a new strategy toward nuclear waste disposal."
In June 2018, the Trump administration and some members of Congress again began proposing using Yucca Mountain, with senators from Nevada raising opposition.
On February 6, 2020, U.S. President Donald Trump tweeted about a potential change of policy on plans to use Yucca Mountain in Nevada as a repository for nuclear waste. Trump's previous budgets have included funding for Yucca Mountain but, according to Nuclear Engineering International, two senior administration officials said that the latest spending blueprint will not include any money for licensing the project. On February 7, Energy Secretary Dan Brouillette echoed Trumps sentiment and stated that the US administration may investigate other types of [nuclear] storage, such as interim or temporary sites in other parts of the country.
Though no formal plan had solidified from the federal government, the private sector is moving forward with their own plans. Holtec International submitted a license application to the US Nuclear Regulatory Commission (NRC) for an autonomous consolidated interim storage facility in southeastern New Mexico in March 2017, which the NRC expects to issue its final environmental impact statement on by March 2021. Similarly, Interim Storage Partners is also planning to build and operate a consolidated interim storage facility in Andrews County, Texas, which the NRC plans to complete their review of in May 2021. Meanwhile, other companies have indicated that they are prepared to bid on an anticipated procurement from the DOE to design a facility for interim storage of nuclear waste.
Deep Isolation company proposed a solution involving horizontal storage of radioactive waste canisters in directional boreholes, using technology developed for oil and gas mining. An 18" borehole is directed vertically to the depth of several thousands feet in geologically stable formations, then horizontal waste disposal section is created of similar length where waste canisters are stored and then borehole is sealed.
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