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The classification of radioactive waste is performed in two stages:

For short-term management, the radioactive waste (both conditioned and non-conditioned) is primarily differentiated on the basis of its activity level and the nature of the radiation emitted;
For long-term management, the conditioned radioactive waste is classified according to its activity level and half-life.



The classification of radioactive waste for short-term management

For short-term management (and in particular for processing and temporary storage), radioactive waste (both conditioned and non-conditioned) is split into three main categories. This categorisation is carried out mainly on the basis of the waste's activity level (i.e. the number of nuclear disintegrations per unit of time) and the nature of the radiation emitted (for example, whether or not there is alpha contamination may affect the way in which the waste is processed). For the transportation and storage of radioactive waste, a third factor is taken into account: the surface contamination level.

These various factors determine the means to be used to ensure protection against the radiation emitted by the waste (shielding and confinement), the protective clothing needed to guarantee the safety of workers and how long workers may remain exposed to radiation without running the risk of being contaminated.

Low-level waste is radioactive waste whose contact dose rate (dose to which an individual is exposed when in contact) is less than 5 milliSieverts per hour. Its production and processing require only minimum shielding measures. Those involved in its processing wear protective clothes, which generally include a plasticized suit, gloves and sometimes a filter mask to ensure the purity of the air they breathe.

This category of waste comes from the generation of electricity by means of nuclear energy (operating of nuclear power plants and production of unspent nuclear fuel), from the use of radioactive sources in medicine, agriculture and industry, and in particular from the decommissioning of nuclear facilities that have been closed down.

These include filters, resins, protective equipment (clothing, gloves, and so on), paper, biological waste, activated concrete, residues from the processing of waste water in nuclear power plants and also decommissioning waste that has been in contact with radioactive substances.

Waste produced by
nuclear power plants
Protective mask nozzles
Syringes


Medium-level waste
is radioactive waste whose contact dose rate is between 5 milliSieverts and 3 Sieverts per hour. It must be processed in an enclosed and shielded area. Workers are protected by concrete walls and armoured glass windows. All operations are performed using remote-controlled devices.

Most of this category of waste comes from the production and reprocessing of nuclear fuel and from decommissioning activities. Some filters and resins from nuclear power plants also belong to this category.


High-level waste is radioactive waste whose contact dose rate is greater than 2 Sieverts per hour. This type of waste emits heat. It is subject to the same precautions as medium-level waste. The only difference is the thickness of the shielding, which is always calculated so as to reduce as much as possible the amount of radiation to which operators are exposed.

This category of waste consists of fission products from the reprocessing of spent nuclear fuel, the spent fuel itself, if it has not been reprocessed, and any other excess fissile materials.

(Photo : the fuel assembly)

In terms of waste volumes, around 75% of radioactive waste is low-level waste and around 1% is highly radioactive (although it represents 95% of total radioactive waste activity, all categories included). The rest is medium-level.



The classification of radioactive waste for long-term management

For long-term management (disposal), ONDRAF/NIRAS has adopted a method for classifying conditioned radioactive waste based on three categories. This classification method is compatible with those of the International Atomic Energy Agency (IAEA) and the European Union. It categorises radioactive waste according to its activity level and life span.

The half-life of radionuclides present in the radioactive waste (the time needed for its level of activity to reduce by half) determines the solutions to be applied for the long-term management of this waste. The objective of radioactive waste management is to at all times prevent such waste from harming man and his environment. The waste is therefore isolated from the biosphere until its activity level has fallen to a level comparable with that of background radiation.


Category A waste
(low or medium-level and short-lived waste)

Category A waste is conditioned waste containing radioelements of a sufficiently low activity level and with a sufficiently short life span to allow surface disposal. It includes low or medium-level and short-lived waste, i.e. waste made up of radioelements of which the majority have a life span of less than or equal to 30 years. These radioelements may contain minute quantities of long-lived alpha emitters.
This category of waste must be isolated from man and the environment for 300 years, which is the time necessary for their activity level to decrease by at least a factor of 1,000.


Category B waste
(low or medium-level and long-lived waste)

Category B waste consists of conditioned low and medium-level waste contaminated by long-lived alpha emitters in quantities that are too great for this waste to be classified as category A, but which emit too little heat to belong to category C. This waste may also contain varying quantities of beta and gamma emitters.

Category C waste
(high-level short or long-lived waste)

Category C waste includes all conditioned high-level waste containing significant amounts of beta and gamma emitters with a short life span and large quantities of long-lived alpha emitters. Because of the high activity level, most waste in this category emits considerable amounts of heat (more than 20 Watt/m³).

Category B and C waste, which contains significant quantities of radioelements of a half-life greater than 30 years, must be isolated from man and the environment for more than 300 years. The time needed for its activity level to decrease by at least a factor of 1,000 may indeed be several tens of thousands of years.

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