Radioactive Waste Management

(Updated 10 April 2017)

  • Nuclear power is the only large-scale energy-producing technology which takes full responsibility for all its wastes and fully costs this into the product.
  • The amount of radioactive wastes is very small relative to wastes produced by fossil fuel electricity generation.
  • Used nuclear fuel may be treated as a resource or simply as a waste.
  • Nuclear wastes are neither particularly hazardous nor hard to manage relative to other toxic industrial wastes.
  • Safe methods for the final disposal of high-level radioactive waste are technically proven; the international consensus is that this should be geological disposal.

All parts of the nuclear fuel cycle produce some radioactive waste (radwaste) and the relatively modest cost of managing and disposing of this is part of the electricity cost (i.e. it is internalised and paid for by the electricity consumers).

At each stage of the fuel cycle there are proven technologies to dispose of the radioactive wastes safely. For low- and intermediate-level wastes, disposal is mostly already being implemented. For high-level wastes some countries await the accumulation of enough material to warrant building geological repositories; others, such as the USA, have encountered political delays.

Unlike other industrial wastes, the level of hazard of all nuclear waste – its radioactivity – diminishes with time. Each radionuclidea contained in the waste has a half-life – the time taken for half of its atoms to decay and thus for it to lose half of its radioactivity. Radionuclides with long half-lives tend to be alpha and beta emitters – making their handling easier – while those with short half-lives tend to emit the more penetrating gamma rays. Eventually all radioactive wastes decay into non-radioactive elements. The more radioactive an isotope is, the faster it decays.

The main objectives in managing and disposing of radioactive (or other) waste are to protect people and the environment. This means isolating or diluting the waste so that the rate or concentration of any radionuclides returned to the biosphere is harmless. To achieve this, practically all wastes are contained and managed, with some clearly needing deep and permanent burial. From nuclear power generation, unlike all other forms of thermal electricity generation, all waste is regulated – none is allowed to cause harmful pollution.

All toxic wastes need to be dealt with safely, not just radioactive wastes. In countries with nuclear power, radioactive wastes comprise less than 1% of total industrial toxic wastes (the balance of which remains hazardous indefinitely).

Types of radioactive waste

Exempt waste & very low-level waste

Exempt waste and very low-level waste (VLLW) contains radioactive materials at a level which is not considered harmful to people or the surrounding environment. It consists mainly of demolished material (such as concrete, plaster, bricks, metal, valves, piping, etc.) produced during rehabilitation or dismantling operations on nuclear industrial sites. Other industries, such as food processing, chemical, steel, etc. also produce VLLW as a result of the concentration of natural radioactivity present in certain minerals used in their manufacturing processes (see also information page on Naturally-Occurring Radioactive Materials). The waste is therefore disposed of with domestic refuse, although countries such as France are currently developing facilities to store VLLW in specifically designed VLLW disposal facilities.

Low-level waste

Low-level waste (LLW) is generated from hospitals and industry, as well as the nuclear fuel cycle. It comprises paper, rags, tools, clothing, filters, etc., which contain small amounts of mostly short-lived radioactivity. It does not require shielding during handling and transport and is suitable for shallow land burial. To reduce its volume, it is often compacted or incinerated before disposal. It comprises some 90% of the volume but only 1% of the radioactivity of all radioactive waste.

Intermediate-level waste

Intermediate-level waste (ILW) contains higher amounts of radioactivity and some requires shielding. It typically comprises resins, chemical sludges and metal fuel cladding, as well as contaminated materials from reactor decommissioning. Smaller items and any non-solids may be solidified in concrete or bitumen for disposal. It makes up some 7% of the volume and has 4% of the radioactivity of all radwaste. By definition, its radioactive decay generates heat of less than about 2 kW/m3 so does not require heating to be taken into account in design of storage or disposal facilities.

High-level waste

High-level waste (HLW) arises from the 'burning' of uranium fuel in a nuclear reactor. HLW contains the fission products and transuranic elements generated in the reactor core. It is highly radioactive and hot due to decay heat, so requires cooling and shielding. It has thermal power above about 2 kW/m3 and can be considered as the 'ash' from 'burning' uranium. HLW accounts for over 95% of the total radioactivity produced in the process of electricity generation. There are two distinct kinds of HLW:

  • Used fuel itself.
  • Separated waste from reprocessing the used fuel.

HLW has both long-lived and short-lived components, depending on the length of time it will take for the radioactivity of particular radionuclides to decrease to levels that are considered non-hazardous for people and the surrounding environment. If generally short-lived fission products can be separated from long-lived actinides, this distinction becomes important in management and disposal of HLW.

HLW is a major focus of attention regarding nuclear power, and is managed accordingly.

Mining and milling

Traditional uranium mining generates fine sandy tailings, which contain virtually all the naturally occurring radioactive elements naturally found in uranium ore. These are collected in engineered tailings dams and finally covered with a layer of clay and rock to inhibit the leakage of radon gas and ensure long-term stability. In the short term, the tailings material is often covered with water. After a few months, the tailings material contains about 75% of the radioactivity of the original ore. Strictly speaking these are not classified as radioactive wastes.

Conversion, enrichment, fuel fabrication

Uranium oxide concentrate from mining, essentially 'yellowcake' (U3O8), is not significantly radioactive – barely more so than the granite used in buildings. It is refined then converted to uranium hexafluoride gas (UF6). As a gas, it undergoes enrichment to increase the U-235 content from 0.7% to about 3.5%. It is then turned into a hard ceramic oxide (UO2) for assembly as reactor fuel elements.

The main byproduct of enrichment is depleted uranium (DU), principally the U-238 isotope, which is stored either as UF6 or U3O8. About 1.2 million tonnes of DU is now stored. Some is used in applications where its extremely high density makes it valuable, such as the keels of yachts and military projectiles. It is also used (with reprocessed plutonium) for making mixed oxide fuel and to dilute highly-enriched uranium from dismantled weapons which is now being used for reactor fuel (see also information pages on Uranium and Depleted Uranium and Military Warheads as a Source of Nuclear Fuel).

Electricity generation

In terms of radioactivity, HLW is the major source arising from the use of nuclear reactors to generate electricity. Highly radioactive fission products and also transuranic elements are produced from uranium and plutonium during reactor operations and are contained within the used fuel. Where countries have adopted a closed cycle and utilised reprocessing to recycle material from used fuel, the fission products and minor actinidesb are separated from uranium and plutonium and treated as HLW (uranium and plutonium is then re-used as fuel in reactors). In countries where used fuel is not reprocessed, the used fuel itself is considered a waste and therefore classified as HLW.

Low- and intermediate-level waste is produced as a result of operations, such as the cleaning of reactor cooling systems and fuel storage ponds, and the decontamination of equipment, filters and metal components that have become radioactive as a result of their use in or near the reactor.

How much waste is produced?

As already noted, the volume of nuclear waste produced by the nuclear industry is small compared with other wastes generated from industrial activity. Each year, nuclear power generation facilities worldwide produce about 154,000 m3 of LLW and ILW, and about 34,000 m3 of HLW (including used fuel designated as waste)1.

In the OECD countries, some 300 million tonnes of toxic wastes are produced each year, but conditioned radioactive wastes amount to only 81,000 m3 per year.

In the UK, for example, the total amount of radioactive waste (including radioactive waste expected to arise from existing nuclear facilities) is about 4.7 million m3, or around 5 million tonnes. A further 1 million m3 has already been disposed. Of the UK's total radioactive waste, about 94% (i.e. about 4.4 million m3) falls into the LLW category. About 6% (290,000 m3) is in the ILW category, and less than 0.1% (1000 m3) is classed as HLW. Although the volume of HLW is relatively small, it contains about 95% of the total inventory of radioactivity12.

A typical 1000 MWe light water reactor will generate (directly and indirectly) 200-350 m3 of LLW and ILW waste per year. It will also discharge about 20 m3 (27 tonnes) of used fuel per year, which corresponds to a 75 m3 disposal volume following encapsulation if it is treated as waste. Where that used fuel is reprocessed, only 3 m3 of vitrified waste (glass) is produced, which is equivalent to a 28 m3 disposal volume following placement in a disposal canister.

This compares with an average 400,000 tonnes of ash produced from a coal-fired plant of the same power capacity. Today, volume reduction techniques and abatement technologies, as well as continuing good practice within the workforce, all contribute to continuing minimisation of waste produced – a key principle of waste management policy in the nuclear industry. Whilst the volumes of nuclear wastes produced are very small, the most important issue for the nuclear industry is managing their toxic nature in a way that is environmentally sound and presents no hazard to both workers and the general public.

Managing high-level waste

Used fuel gives rise to HLW which may be either the used fuel itself in fuel rods, or the separated waste arising from reprocessing (see also information page on Processing of Used Nuclear Fuel). In either case, the amount is modest – as noted above, a typical reactor generates about 27 tonnes of used fuel which may be reduced to 3 m3 per year of vitrified waste. Both can be effectively and economically isolated, and have been handled and stored safely since nuclear power began.

Storage of used fuel is mostly in ponds associated with individual reactors, or in a common pool at multi-reactor sites, or occasionally at a central site.

If the used fuel is reprocessed, as is that from UK, French, German, Japanese and Russian reactors, HLW comprises highly-radioactive fission products and some transuranic elements with long-lived radioactivity. These are separated from the used fuel, enabling the uranium and plutonium to be recycled. Liquid HLW from reprocessing must be solidified. The HLW also generates a considerable amount of heat and requires cooling. It is vitrified into borosilicate (Pyrex) glass, sealed into heavy stainless steel cylinders about 1.3 metres high, and stored for eventual disposal deep underground. This material has no conceivable future use and is unequivocally waste.

The hulls and end-fittings of the reprocessed fuel assemblies are compacted, to reduce volume, and usually incorporated into cement prior to disposal as ILW. France has two commercial plants to vitrify HLW left over from reprocessing oxide fuel, and there are also plants active in the UK and Russia.

If used reactor fuel is not reprocessed, it will still contain all the highly radioactive isotopes. Spent fuel that is not reprocessed is treated as HLW for direct disposal. It too generates a lot of heat and requires cooling. However, since it largely consists of uranium (with a little plutonium), it represents a potentially valuable resource, and there is an increasing reluctance to dispose of it irretrievably.

Either way, after 40-50 years the heat and radioactivity have fallen to one thousandth of the level at removal. This provides a technical incentive to delay further action with HLW until the radioactivity has reduced to about 0.1% of its original level.

After storage for about 40 years the used fuel assemblies are ready for encapsulation or loading into casks ready for indefinite storage or permanent disposal underground.

Direct disposal of used fuel has been chosen by the USA and Sweden, among others, although evolving concepts lean towards making it recoverable if future generations see it as a resource. This means allowing for a period of management and oversight before a repository is closed.

Used fuel is subject to international safeguards due to its uranium and plutonium content. Separated (and vitrified) HLW is not subject to safeguards, which is another factor in easier handling.

Decay in radioactivity of fission products

One tonne of spent PWR fuel

Both direct disposal and reprocessing are in accordance with the definition of sustainable used fuel management set out by the World Nuclear Association.*

* The World Nuclear Association considers used fuel management to be sustainable if it meets the following key criteria:

  • It covers all the steps of used fuel management from the generation of used fuel up to and including final disposal in accordance with a well-defined practical plan.
  • It proves to be feasible with a sustainable impact level.
  • It includes a realistic financing plan.
  • It is able to demonstrate to a practicable extent that it is technically and economically viable.
  • It protects human health and the environment and has no greater impact on the health of future generations than is allowed today.
  • It answers to a present need but does not impose burdens on future generations.

Due to the long-term nature of these management plans, sustainable options must have one or more pre-defined milestones where a decision could be taken on which option to proceed with.

Recycling used fuel

Any used fuel will still contain some of the original U-235 as well as various plutonium isotopes which have been formed inside the reactor core, and the U-238c. In total these account for some 96% of the original uranium and over half of the original energy content (ignoring U-238). Reprocessing, undertaken in Europe and Russia, separates this uranium and plutonium from the wastes so that they can be recycled for re-use in a nuclear reactor (see also information page on Processing of Used Nuclear Fuel). Plutonium arising from reprocessing is recycled through a MOX fuel fabrication plant where it is mixed with depleted uranium oxide to make fresh fuel (see also information page on Mixed Oxide Fuel). European reactors currently use over 5 tonnes of plutonium a year in fresh MOX fuel.

Major commercial reprocessing plants operate in France, the UK, and Russia with a capacity of some 5000 tonnes per year and cumulative civilian experience of 80,000 tonnes over 50 years. A new reprocessing plant with an 800 t/yr capacity is undergoing commissioning at Rokkasho in Japan. France and the UK also undertake reprocessing for utilities in other countries, notably Japan, which has made over 140 shipments of used fuel to Europe since 1979. Until now most Japanese used fuel has been reprocessed in Europe, with the vitrified waste and the recovered uranium and plutonium (as MOX fuel) being returned to Japan to be used in fresh fuel (see also information page on Japanese Waste and MOX Shipments From Europe). Russia also reprocesses some used fuel from Soviet-designed reactors in other countries.

There are several proposed developments of reprocessing technologies (see also information page on Processing of Used Nuclear Fuel). One technology under development would separate plutonium along with the minor actinides as one product. This however cannot be simply put into MOX fuel and recycled in conventional reactors; it requires fast neutron reactors which are as of yet not common. On the other hand, if proved commercially, it will make disposal of HLW easier.

The options for used fuel are:

  • Direct disposal (after storage) to a geological repository. The material has very long-lived radioactivity, and will take about 300,000 years to reach the same level as the original ore.
  • Aqueous reprocessing to remove only uranium and plutonium. The material then only takes about 9000 years to reach the same level of radioactivity as the original ore.
  • Advanced electrometallurgical reprocessing which removes uranium, plutonium and minor actinides together for recycling in a fast reactor. The wastes then only need 300 years to reach the same level of radioactivity as the original ore. This is not yet operational on any commercial scale.

THORP Fuel Storage

Storage pond for used fuel at the Thermal Oxide Reprocessing Plant at the UK's Sellafield site (Sellafield Ltd)

Storage and disposal of used fuel and separated HLW

There is about 240,000 tonnes of used fuel in storage, much of it at reactor sites. About 90% of this is in storage ponds (smaller versions of that illustrated above), with the balance in dry storage. Annual additions of used fuel are about 7,000 tonnes (6,000 t from LWRs), and up to 3,000 tonnes of this are intended for reprocessing. Final disposal is not urgent in any logistical sense.

According to GE Hitachi, in 2015 funds set aside for managing and disposal of used fuel totalled about $100 billion (most notably $51 billion of this in Europe, $40 billion in the USA and $6.5 billion in Canada).

Storage ponds at reactors, and those at centralized facilities such as CLAB in Sweden, are 7-12 metres deep, to allow for several metres of water over the used fuel (assembled in racks typically about 4 metres long and standing on end). The multiple racks are made of metal with neutron absorbers incorporated. The circulating water both shields and cools the fuel. These pools are robust constructions made of thick reinforced concrete with steel liners. Ponds at reactors are often designed to hold all the used fuel produced over the planned operating life of the reactor.

Some fuel that has been cooling in ponds for at least five years is stored in dry casks or vaults with air circulation inside concrete shielding. One common system is for sealed steel casks or multi-purpose canisters (MPCs) each holding up to about 40 fuel assemblies with inert gas. Casks/MPCs may be used also for transporting and eventual disposal of the used fuel. For storage, each is enclosed in a ventilated storage module made of concrete and steel. These are commonly standing on the surface, about 6m high, cooled by air convection, or they may be below grade, with just the tops showing. The modules are robust and provide full shielding. Each cask has up to 45 kW heat load.

A collection of casks or modules comprises an Independent Spent Fuel Storage Installation (ISFSI), which in the USA is licensed separately from any associated power plant, and is for interim storage only. About one-quarter of US used fuel is in such installations.

For disposal, to ensure that no significant environmental releases occur over tens of thousands of years, 'multiple barrier' geological disposal is planned. This immobilises the radioactive elements in HLW and some ILW and isolates them from the biosphere. The main barriers are:

  • Immobilise waste in an insoluble matrix such as borosilicate glass or synthetic rock (fuel pellets are already a very stable ceramic: UO2).
  • Contain waste sealed inside a corrosion-resistant container, such as stainless steel.
  • Isolate waste from people and the environment, so eventually locate it deep underground in a stable rock structure.
  • Delay any significant migration of radionuclides from the repository, so surround containers with an impermeable backfill such as bentonite clay if the repository is wet.


Loading silos with canisters containing vitrified HLW in the UK. Each disc on the floor covers a silo holding ten canisters

HLW from reprocessing must be solidified. France has two commercial plants to vitrify HLW left over from reprocessing oxide fuel, and there are also significant plants in the UK and Belgium. The capacity of these western European plants is 2,500 canisters (1000 t) a year, and some have been operating for three decades. By mid-2009, the UK Sellafield vitrification plant had produced its 5000th canister of vitrified HLW, representing 3000 m3 of liquor reduced to 750 m3 of glass. The plant fills about 400 canisters per year.

The Australian Synroc (synthetic rock) system is a more sophisticated way to immobilise such waste, and this process may eventually come into commercial use for civil wastes (see also appendix on Synroc).

To date there has been no practical need for final HLW repositories, as surface storage for 40-50 years is first required so that heat and radioactivity can decay to levels which make handling and storage easier.

The process of selecting appropriate deep geological repositories is now underway in several countries. Finland and Sweden are well advanced with plans for direct disposal of used fuel in mined repositories, since their parliaments decided to proceed on the basis that it was safe, using existing technology. Both countries have selected sites. In Sweden the location was decided after competition between two municipalities. The USA has opted for a final repository at Yucca Mountain in Nevada, though this is now stalled due to political decision. There have also been proposals for international HLW repositories in optimum geology2. (See also page on International Nuclear Waste Disposal Concepts).

Relative activity of used fuel with 38 GWd/t burn-up

Relative activity of used fuel with 38 GWd/t burn-up

Source: IAEA (referenced in Radioactive Waste in Perspective NEA 2010, p74)

A current question is whether wastes should be emplaced so that they are readily retrievable from repositories. There are sound reasons for keeping such options open – in particular, it is possible that future generations might consider the buried waste to be a valuable resource. On the other hand, permanent closure might increase long-term security of the facility. After being buried for about 1,000 years most of the radioactivity will have decayed. The amount of radioactivity then remaining would be similar to that of the naturally-occurring uranium ore from which it originated, though it would be more concentrated. In mined repositories, which represent the main concept being pursued, retrievability can be straightforward, but any deep borehole disposal is permanent.

Deep boreholes are more appropriate for smaller amounts of wastes than national programs involving direct disposal of used fuel, and hence are more likely to be used for smaller volumes of shorter-lived wastes arising from Generation IV fuel cycles.

France's 2006 waste law says that HLW disposal must be 'reversible', which was clarified in a 2015 amendment to mean guaranteeing long-term flexibility in disposal policy, while 'retrievable' referred to short-term practicality. France, Switzerland, Canada, Japan and the USA require retrievability. That policy is followed also in most other countries, though this presupposes that in the long-term, the repository would be sealed to satisfy safety requirements.

The measures or plans that various countries have in place to store, reprocess and dispose of used fuel and wastes are described in Appendix 2: National Policies and summarised in the following Table. Storage and disposal options are described more fully in the information page on Storage and Disposal of Radioactive Wastes.

Waste management for used fuel and HLW from nuclear power reactors

Country Policy Facilities and progress towards final repositories
Belgium Reprocessing
but moving to direct disposal
  • Central waste storage at Dessel
  • Underground laboratory established 1984 at Mol
  • Construction of repository to begin about 2035
Canada Direct disposal
  • Nuclear Waste Management Organisation (NWMO) set up 2002
  • Deep geological repository confirmed as policy, retrievable
  • Repository site search from 2007, planned for operation by 2035
China Reprocessing
  • Central used fuel storage at LanZhou in central Gansu province
  • Repository site search from 1986, selection to be completed by 2020
  • Underground research laboratory 2015-20, disposal of HLW from 2050
Finland Direct disposal
  • Program start 1983, Posiva Oy set up 1995 to implement confirmed policy of deep geological disposal
  • Underground research laboratory Onkalo under construction since 2004
  • Repository being built from this, near Olkiluoto, to open in 2023
France Reprocessing
  • Underground rock laboratories in clay and granite
  • Parliamentary confirmation in 2006 of deep geological disposal, containers to be retrievable and policy 'reversible'
  • Construction and operating licence for Bure expected in 2018, construction to start 2020
Germany Reprocessing
but moving to direct disposal
  • Repository planning started 1973
  • Used fuel storage at Ahaus and Gorleben salt dome
  • Geological repository may be operational at Gorleben after 2025, decision due 2019
India Reprocessing
  • Research on deep geological disposal for HLW
Japan Reprocessing
  • Used fuel and HLW storage facility at Rokkasho since 1995
  • Underground laboratory at Mizunami in granite since 1996
  • Used fuel storage built at Mutsu, expected to open 2018
  • NUMO set up 2000, site selection for deep geological repository under way to 2025, operation from 2035, retrievable
Russia Reprocessing
  • NO RAO set up in 2012 to manage HLW and its disposal
  • Underground laboratory in granite or gneiss in Krasnoyarsk region from 2015, may evolve into repository by 2024
  • Pool storage for used VVER-1000 fuel at Zheleznogorsk since 1985
  • Dry storage for used RBMK and other fuel at Zheleznogorsk from 2012
  • Various interim storage facilities in operation
South Korea Direct disposal, wants to change
  • Waste program confirmed 1998, Korean Radioactive Waste Management Co. (KRWM) set up 2009
  • Mid-2013 KRWM rebranded as Korean Radioactive Waste Agency (KORAD)
  • Central interim storage facility pending construction
Spain Direct disposal
  • ENRESA established 1984, its plan accepted 1999
  • Central interim storage at Villar de Canas from 2016 (volunteered location)
  • Research on deep geological disposal
Sweden Direct disposal
  • Central used fuel storage facility – CLAB – in operation since 1985 at Oskarshamn
  • Underground research laboratory at Aspo for HLW repository
  • Osthammar site selected for repository (volunteered location), likely to open in 2028
Switzerland Reprocessing
  • Central interim storage for HLW and used fuel at ZZL Wurenlingen since 2001
  • Smaller used fuel storage at Beznau
  • Underground research laboratory for high-level waste repository at Grimsel since 1983
United Kingdom Reprocessing


  • HLW from reprocessing is vitrified and stored at Sellafield
  • Repository location to be on basis of community agreement
  • New NDA subsidiary to progress geological disposal
USA Direct disposal
  • Policy since 1977 to forbid reprocessing
  • DoE responsible for used fuel from 1998, accumulated $40 billion waste fund
  • Considerable research and development on repository in welded tuffs at Yucca Mountain, Nevada
  • The 2002 Congress decision that geological repository be at Yucca Mountain was countered politically in 2009
  • Central interim storage for used fuel now likely

Note: in most countries repositories, or at least storage facilities, for LLW and ILW are operating. See also individual Country Profiles.

Wastes from decommissioning nuclear plants

In the case of nuclear reactors, about 99% of the radioactivity is associated with the fuel. Apart from any surface contamination of plant, the remaining radioactivity comes from 'activation products' such as steel components which have long been exposed to neutron irradiation. Their atoms are changed into different isotopes such as iron-55, cobalt-60, nickel-63 and carbon-14. The first two are highly radioactive, emitting gamma rays, but with correspondingly short half-lives so that after 50 years from final shutdown their hazard is much diminished. Some caesium-137 may also be found in decommissioning wastes.

Some scrap material from decommissioning may be recycled, but for uses outside the industry very low clearance levels are applied, so most is buried and some is recycled within the industry.

Generally, short-lived ILW (mainly from decommissioning reactors) is buried, while long-lived ILW (from fuel reprocessing) will be disposed of deep underground. LLW is disposed of in shallow burial sites.

Disposal of other radioactive wastes

Some low-level liquid wastes from reprocessing plants are discharged to the sea. These include radionuclides which are distinctive, notably technetium-99 (sometimes used as a tracer in environmental studies), and this can be discerned many hundred kilometres away. However, such discharges are regulated and controlled, and the maximum radiation dose anyone receives from them is a small fraction of natural background radiation.

Nuclear power stations and reprocessing plants release small quantities of radioactive gases (e.g. krypton-85 and xenon-133) and trace amounts of iodine-131 to the atmosphere. However, krypton-85 and xenon-133 are chemically inert, and all three gases have short half-lives, and the radioactivity in the emissions is diminished by delaying their release. The net effect is too small to warrant consideration in any life-cycle analysis. A little tritium is also produced but regulators do not consider its release to be significant.

The US Nuclear Regulatory Commission classifies LLW into four categories based on radioactivity corresponding to management and disposal requirements:

  • Class A waste has the lowest radioactivity level and decays to background level after about 100 years. It accounts for about 99% of the volume of LLW generated in the USA and includes slightly contaminated paper products, clothing, rags, mops, equipment and tools, as well as depleted uranium.
  • Class B and C wastes include filters, resins, irradiated hardware with activation products, and longer-lived radioisotopes that decay after 300 and 500 years, respectively.
  • Greater-than-Class C LLW has radionuclide concentration limits greater than those specified for Class C waste.

Following the Fukushima accident, large areas were contaminated mainly with caesium fallout. In 2016 the government announced that material with less than 8 kBq/kg caesium would no longer be subject to restriction regarding disposal or use for embankments. This is about six times the average radioactivity of the Earth’s crust and about three times the average radioactivity of Australian coal ash.

It is noteworthy that coal burning produces some 280 million tonnes of ash per year, most of it containing low levels of natural radionuclides3. Some of this could be classified as LLW. It is simply buried (see also information page on Naturally-Occurring Radioactive Materials).

Costs of radioactive waste management

Financial provisions are made for managing all kinds of civilian radioactive waste. The cost of managing and disposing of nuclear power plant wastes represents about 5% of the total cost of the electricity generated.

Most nuclear utilities are required by governments to put aside a levy (e.g. 0.1 cents per kilowatt hour in the USA to 2014, 0.14 ¢/kWh in France) to provide for management and disposal of their wastes (see also appendix on National Funding). So far some US$ 40 billion has been accumulated in the US waste fund from electricity consumers, including some interest.

The actual arrangements for paying for waste management and decommissioning also vary. The key objective is however always the same: to ensure that sufficient funds are available when they are needed. There are three main approaches4:

Provisions on the balance sheet

Sums to cover the anticipated costs of waste management and decommissioning are included on the generating company's balance sheet as a liability. As waste management and decommissioning work proceeds, the company has to ensure that it has sufficient investments and cashflow to meet the required payments.

Internal fund

Payments are made over the life of the nuclear facility into a special fund that is held and administered within the company. The rules for the management of the fund vary, but many countries allow the fund to be re-invested in the assets of the company, subject to adequate securities and investment returns.

External fund

Payments are made into a fund that is held outside the company, often within government or administered by a group of independent trustees. Again, rules for the management of the fund vary. Some countries only allow the fund to be used for waste management and decommissioning purposes, others allow companies to borrow a percentage of the fund to reinvest in their business.

Natural precedents for geological disposal

Nature has already proven that geological isolation is possible through several natural examples (or 'analogues'). The most significant case occurred almost 2 billion years ago at Oklo in what is now Gabon in West Africa, where several spontaneous nuclear reactors operated within a rich vein of uranium ore5.(At that time the concentration of U-235 in all natural uranium was about 3%.) These natural nuclear reactors continued for about 500,000 years before dying away. They produced all the radionuclides found in HLW, including over 5 tonnes of fission products and 1.5 tonnes of plutonium, all of which remained at the site and eventually decayed into non-radioactive elements.

The study of such natural phenomena is important for any assessment of geologic repositories, and is the subject of several international research projects. However, it must be noted that the Oklo reactions proceeded because groundwater was present as a moderator in the 'enriched' and permeable uranium ore.

Legacy wastes

In addition to the routine wastes from current nuclear power generation there are other radioactive wastes referred to as 'legacy wastes'. These wastes exist in several countries which pioneered nuclear power and especially where power programmes were developed out of military programmes. These are sometimes voluminous and difficult to manage, and arose in the course of those countries getting to a position where nuclear technology is a commercial proposition for power generation. They represent a liability which is not covered by current funding arrangements. In the UK, some £73 billion (undiscounted) is estimated to be involved in addressing these wastes6 – principally from Magnox and some early AGR developments – and about 30% of the total is attributable to military programs. In the USA, Russia and France the liabilities are also considerable.


The nuclear and radioactive waste management industries work to well-established safety standards for the management of radioactive waste. International and regional organisations such as the International Atomic Energy Agency (IAEA), the Nuclear Energy Agency (NEA) of the Organisation for Economic Co-operation and Development (OECD), the European Commission (EC) and the International Commission on Radiological Protection (ICRP) develop standards, guidelines and recommendations under a framework of co-operation to assist countries in establishing and maintaining national standards. National policies, legislation and regulations are all developed from these internationally agreed standards, guidelines and recommendations. Amongst others, these standards aim to ensure the protection of the public and the environment, both now and into the future.

International agreements in the form of conventions have also been established such as the Joint Convention on Nuclear Safety, and the Joint Convention on the Safety of Spent Fuel Management and on the Safety of Radioactive Waste Management. The latter was adopted in 1997 by a diplomatic conference convened by the IAEA and came into force in June 2001 following the required number of ratifications.

Other international conventions and directives seek to provide for inter alia, the safe transportation of radioactive material, protection of the environment (including the marine environment) from radioactive waste, and the control of imports and exports of radioactive waste and transboundary movements.

International Atomic Energy Agencyd

The IAEA is the international organisation that advises on the safe and peaceful uses of nuclear technology. It is an agency of the United Nations, based in Vienna, Austria founded in 1957 and it currently has 134 member states from countries with and without nuclear energy programmes. The IAEA develops safety standards, guidelines and recommendations and, inter alia, provides technical guidance to member states on radioactive waste principles. Member states use the standards and guidelines in developing their own legislation, regulatory documents and guidelines. It also verifies through a safeguards inspection programme compliance with the Nuclear Non-Proliferation Treaty (NPT) (see also information page on Safeguards to Prevent Nuclear Proliferation).

The IAEA's Waste and Environmental Safety Section works to develop internationally agreed standards on the safety of radioactive waste. The Radioactive Waste Safety Standards Programme (RADWASS) provides guidance to member states to produce their own policies and regulations for the safe management of radioactive waste, including disposal7.

In addition, the IAEA helps member states by providing technical assistance with services, equipment and training and by conducting radiological assessments.

Nuclear Energy Agencye

The Nuclear Energy Agency of the OECD is based in Paris, France. It has a variety of waste management programmes involving its 28 member states. The organisation aims to assist these states in developing safe waste disposal strategies and policies for spent nuclear fuel, HLW and waste from decommissioning nuclear facilities. It also works closely with the IAEA on nuclear safety standards and other technical activities.

The NEA has a project aimed at preserving records, knowledge and management (RK&M) of long-lived nuclear waste disposal for future generations.

European Commission

For several years, the European Commission (EC) has attempted to pass Directives aimed at ensuring a common approach to nuclear safety and radioactive waste management. The so-called 'Nuclear Package' of Directives on nuclear safety and waste management was a top-down approach which met with considerable opposition from several Member States and was revised on several occasions leading to the 2011 adoption of a scaled-back version.8

In July 2011 the European Union adopted a directive for the disposal of used nuclear fuel and radioactive wastes which required member countries to develop national waste management plans for European Commission review by 2015. The plans must include firm timetables for the construction of disposal facilities, descriptions of needed implementation activities, cost assessments, and financing schemes. Safety standards promulgated by the IAEA would become legally binding within the EU-wide policy framework. International peer reviews should be invited at least every ten years.

The agreement allows two or more member nations to develop joint disposal facilities and allows transport of used fuel and radioactive wastes within the EU. Exports outside the EU will only be possible to countries that already have a repository in operation that meets IAEA standards. For overseas reprocessing, ultimate wastes must be returned to the originating EU country. The directive acknowledges that no country currently operates such a repository and projects that a minimum of 40 years would be required to develop one. The shipment of used fuel and radioactive wastes to African, Pacific and Caribbean countries and to Antarctica is explicitly banned. Plans are expected to use a step-by-step approach to geologic disposal based on the voluntary involvement of potential host communities. Two routes are acknowledged: one to dispose of used nuclear fuel as waste; the other to reprocess the fuel and recycle the uranium and plutonium while disposing of the remainder as waste.

The directive became effective in August 2011, and national governments, which retain ultimate responsibility for wastes, had two years to bring their nuclear waste legislation into line with it. There are 143 nuclear energy facilities generating used fuel in 14 of the EU’s 27 member nations. The remaining nations possess radioactive waste requiring disposal that has been produced by research, medicine and industry.

International Commission on Radiological Protectionf

The International Commission on Radiological Protection (ICRP) is an independent registered charity that issues recommendations for protection against all sources of radiation. The IAEA interprets these recommendations into international safety standards and guidelines for radiological protection. National regulators may also adopt the recommendations by the ICRP for their own radiation protection standards.

In March 2007, the ICRP approved its new fundamental Recommendations on radiological protection (ICRP Publication 103)11, replacing the Commission’s previous Recommendations from 1990. Amongst others, the new recommendations include for the first time an approach for developing a framework to demonstrate radiological protection of the environment.


Nuclear wastes are a significant part of the nuclear power picture, and need to be managed and disposed of properly. However in more than 50 decades of civil nuclear power experience they have not caused any serious health or environmental problems, nor posed any real risks to people.

Alternatives for power generation are not without challenges, and for a variety of reasons they – particularly those from coal combustion – have not always been well controlled. Both flyash and bottom ash are often loaded with heavy metals including uranium and thorium (see also page on NORM). Flyash is mostly retained for land disposal today, and bottom ash is normally buried also, but not always securely/without effects on groundwater. Groundwater pollution with arsenic, boron, cobalt and mercury is not unusual, and the US EPA in 2011 listed 181 US coal ash ponds which posed a significant hazard, 47 of these a high hazard and threat to life. Duke Energy in North Carolina expects to spend some $6 billion on clean-up of coal ash. Burning any fossil fuels gives rise to carbon dioxide emissions, and gaseous pollutants such as nitrogen oxides and often sulfur oxides. About one-quarter of anthropogenic mercury emissions are attributed to burning coal, with up to 70% originating in North America.

Non-nuclear radioactive wastes

In recent years, in both the radiological protection and radioactive waste management communities, there has been increased attention on how to effectively manage non‑nuclear radioactive wastes. All countries, including those that do not have nuclear power plants, have to manage radioactive waste generated by activities unrelated to the production of nuclear energy, including: national laboratory and university research activities; used and lost industrial gauges and radiography sources; and nuclear medicine activities at hospitals. Although much of this waste is not long-lived, the variety of the sources makes any general assessment of physical or radiological characteristics difficult. The relatively source‑specific nature of the waste poses questions and challenges for its management at a national level, both in regulatory and practical terms.

Further Information


a. A radionuclide is a radioactive isotope of a particular element. Different isotopes of a given element have different numbers of neutrons, but the same number of protons; hence, isotopes of the same element share atomic numbers but not mass numbers.

b. Uranium and plutonium are members of the actinide group, which comprises the 15 successive chemical elements from actinium on the periodic table. The so-called 'minor actinides' are the actinides present in used nuclear fuel other than uranium and plutonium.

c. Used fuel from light water reactors contains approximately:

95.6% uranium (less than 1% of which is U-235)
2.9% stable fission products
0.9% plutonium
0.3% caesium & strontium (fission products)
0.1% iodine and technetium (fission products)
0.1% other long-lived fission products
0.1% minor actinides (americium, curium, neptunium)

Increasingly, reactors are using fuel enriched to over 4% U-235 and burning it longer, to end up with less than 0.5% U-235 in the used fuel. This provides less incentive to reprocess.

d. See the home page of the IAEA's Division of Radiation, Transport and Waste Safety ( for further information.

e. See the radioactive waste management section of the NEA's website ( for further information.

f. See the International Commission on Radiological Protection's website ( for further information.


1. Estimation of Global Inventories of Radioactive Waste and Other Radioactive Materials, IAEA (2007).

2. Europe steps towards shared repository concept, World Nuclear News (11 February 2009).

3. The U.S. Geological Survey has published a fact sheet on Radioactive Elements in Coal and Fly Ash: Abundance, Forms, and Environmental Significance, FS-163-97 (October 1997).

4. The Economics of the Nuclear Fuel Cycle, Nuclear Energy Agency (1994).

5. Information on the Oklo natural reactors is on the Swedish Nuclear Fuel and Waste Management Company (Svensk Kärnbränslehantering, SKB) website ( See also I. Gurban and M. Laaksoharju, Uranium transport around the reactor zone at Okelobondo (Oklo), Data evaluation with M3 and HYTEC, SKB Technical Report TR-99-36 (December 1999).

6. NDA gives revised UK clean-up cost estimates, World Nuclear News (18 July 2008); The Nuclear Decommissioning Authority – Taking Forward Decommissioning, Report by the Comptroller and Auditor General, National Audit Office (30 January 2008).

7. Dominique Delattre, RADWASS Update, IAEA Bulletin, Volume 42, Number 3 (2000).

8. EC pushes common standards again, Nuclear Engineering International (February 2007); De Palacio's nuclear legacy, Nuclear Engineering International (September 2004).

11. International Commission on Radiological Protection, ICRP Publication 103: Recommendations of the ICRP, Annals of the ICRP Volume 37/2-4, Elsevier (2008). (ISBN: 9780702030482).

12. Department of Energy and Climate Change (DECC) and the Nuclear Decommissioning Authority (NDA), Radioactive Wastes in the UK: A Summary of the 2010 Inventory, (February 2011).

General sources

The International Nuclear Society Council (INSC, has published information relating to particular countries' waste policies and actions. See the Radioactive Waste paper from the report of its 1997-98 Action Plan and its Current Issues in Nuclear Energy – Radioactive Waste report (August 2002)

The management of low- and intermediate-level radioactive waste, Nuclear Energy Agency, NEA Issue Brief: An analysis of principal nuclear issues, No. 6 (August 1989)

Storage and Disposal of Spent Fuel and High Level Radioactive Waste, International Atomic Energy Agency

Association for Regional and International Underground Storage website (

UNSCEAR (United Nations Scientific Committee on the Effects of Atomic Radiation) website (

Assessment of Disposal Options for DOE-Managed High-Level Radioactive Waste and Spent Nuclear Fuel, October 2014, US DOE
Radioactive Waste in Perspective, OECD Nuclear Energy Agency, NEA No. 6350 (2010)


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