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Waste sources and classification

 

17

Table 2.3

 

 

 

 

 

 

(Continued )

 

 

 

 

 

 

 

 

 

 

 

 

 

Nuclide

Half-life (y)

Dec.

Nuclide type

Produced

Percentage

Relevance

 

 

 

 

from

of total

 

 

 

 

 

 

or activity

 

 

 

 

 

 

in spent

 

 

 

 

 

 

fuel (40y)

 

 

 

 

 

 

 

 

Pu-241

14.4

 

AC

 

11.2 ( )

criticality

Pu-242

3.8Eþ05

 

AC

 

 

 

Am-241

432

 

AC

Pu-240

43.0 ( )

heat output

Am-242m

141

 

AC

Am-241

 

 

Am-243

7370

 

AC

Am-241

 

 

Cm-242

0.45

 

AC

 

 

n-dose rate

Cm-243

29.1

 

AC

 

 

 

Cm-244

18.1

 

AC

 

11.5 ( )

n-dose

 

 

 

 

 

 

rate, heat

 

 

 

 

 

 

output

Cm-245

8500

 

AC

Pu-239

 

 

Cm-246

4730

 

AC

 

 

 

 

 

 

 

 

 

 

Fig. 2.6. Typical wastes from reactor operations (image courtesy of ANDRA).

2.4.1.4. Reprocessing

A SF assembly essentially consists of a large number of long rods (containing the spent fuel pellets), which are held in place by grids and relatively large metallic end and bottom pieces. The objective of reprocessing is to separate the fission and transuranic elements (4 per cent) from the uranium (95 per cent) and plutonium (1 per cent) contained within the spent fuel pellets (Fig. 2.7). In relation to the 25 tonnes of fuel mentioned above, reprocessing would result in 1 tonne of fission products and transuranics, 23.75 tonnes of uranium and 0.25 tonnes of plutonium.

18

D.F. McGinnes

Fig. 2.7. A simplified overview of the reprocessing process (image courtesy of AREVA-NC).

The commercial process basically consists of chopping the fuel rods into small pieces and dissolving the fuel pellets in concentrated nitric acid. The liquid containing the waste fission products and transuranics is then separated from the uranium and plutonium. Following this, the uranium and plutonium are then separated from each other, purified and re-used. The high-level waste liquid containing the fission products and actinide (both transuranics and residual uranium and plutonium) isotopes is dried by a calcination process to produce a solid which is then mixed with borosilicate glass and vitrified. The resulting glass is then cast into stainless steel containers and stored. For geological disposal, it is envisaged that each of these containers will be separately placed in a massive metal container (overpack) (e.g., steel in the Swiss and Japanese concepts (Nagra, 1985; JNC, 2000), copper in the Swedish (Werme, 1998) and Finnish (Raiko and Salo, 1999) concepts – see also Chapter 5 for further details).

After dissolution of the spent fuel, the remaining fuel structural materials (Fig. 2.8) and heavily contaminated materials (such as pumps, clothing, etc.) and process residues (effluent treatment) are conditioned as L/ILW-LL. Other wastes, such as lightly contaminated materials, are conditioned and disposed of as L/ILW-SL.

2.4.1.5. Reactor decommissioning

On closure of nuclear facilities, the buildings are generally decontaminated and dismantled. In the case of NPPs, the first stage of decommissioning consists of the removal of all of the SF, accounting for 99 per cent of the radioactivity, from the facility. This then allows the facility to move from an operating to a decommissioning licence. Following this, the reactor (Fig. 2.9) is then completely dismantled to a greenfield site (with no conditions on its subsequent use), with the number of stages and the amount of time required to reach this final stage being dependent on the approved strategy.

Waste sources and classification

19

Fig. 2.8. Reprocessing waste – LILW-LL hulls (image courtesy of AREVA-NC).

The majority of radioactive waste generated from decommissioning activities arises from contaminated or activated components and is conditioned as L/ILW-SL. Depending on national regulations and initial impurity levels (especially uranium and thorium), some of the reactor core components may be classified as L/ILW-LL. A large amount of the waste from the decommissioning of nuclear facilities is generated from the dismantling of support buildings that are not exposed to radiation or any radioactive material, such as office buildings. These facilities can be decommissioned using conventional techniques and the resulting waste can either be recycled or disposed of at a conventional landfill site.

A modern light water reactor would be expected to produce 10 t of decommissioning waste per MW(e) of installed capacity, which equates to around 10,000 t of waste in the 1 GW(e) case (NEA, 2003).

PWR reactor coolant system and its main components

5

1 Reactor vessel

2 Control rod drive mechanisms

3

3 Steam generator

2

4 Reactor coolant pump

4

5 Pressurizer

1

Fig. 2.9. (Continued)

PWR reactor pressure vessel (and equipments)

to hold the reactor core and the surrounding structures

to withstand the hight presure

(155 bar) of the core collant circulating water (around 300°c)

nominal and transient pressures and temperatures

neutron irradiation

low alloy Carbon steel with a stainless steel layer inside

height:12 to 13 meters

internal diameter: 4 to 4.5 meters thickness: 13 to 20 centimeters weight: 330 to 460 metric tons

PWR pressure vessel internals

to support and maintain laterally the fuel

assemblies

to guide the control rods and the internal

instrumentation

to distribute the coolant flow within the core

mechanical effects of the coolant flow

circulation

chemical effect of the collant fluid irradiation

nominal and transient temperatures

stainless steel and Nickel based alloys

height: 12 to 13 meters diameter: 4 to 4.5 meters weight: 160 to 230 metric tons

Design Commissioning

Heat transfer surface: 4,700 to 7,000

square meters

PWR steam generator

Pressurizer

 

Design

to transfer heat and ensure leak-tightness between the primary (P) and secondary (S) circuits

mechanical effects of the circulating P and S flows

chemical effects of the P and S fluids nominal and transient temperatures and pressures on P and S sides

Nickel based alloy (tubes),

low internal alloy Carbon steel (structures) with a stainless steel layer the water chamber (P side)

height: 20 to 22 meters diameter: 3.5 to 5 meters

weight (empty): 300 to 420 metric tons

Commissioning

to maintain constant the pressure in the reactor coolant system

nominal and transient temperatures and pressures

chemical effects of the primary fluid

low alloy Carbon steel

height: 13 meters diameter: 2.5 to 3 meters

weight (empty(: 70 to 120 metric tons

20

McGinnes .F.D

Fig. 2.9. Main components of a pressurised water reactor (PWR) (image courtesy of AREVA-NC).