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RD&D-Programme 2004 - SKB

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Siting<br />

<strong>SKB</strong>’s main alternative is to build the encapsulation plant adjacent to Clab so that it can be<br />

coordinated with existing activities. The spent fuel can then be transferred directly from the<br />

storage pools in Clab to the pools in the encapsulation plant. At Clab there are also personnel<br />

with expertise in and experience from radiological work.<br />

<strong>SKB</strong> has conducted a feasibility study of a standalone encapsulation plant /1-1/ as well as a<br />

comparison between different alternative sitings /1-2/. The standalone encapsulation plant is<br />

assumed to be located near the deep repository’s surface facility. The primary technical difference<br />

between the planned encapsulation plant at Clab and the one at the deep repository is the<br />

way in which the fuel is handled and prepared prior to encapsulation. In the latter case, pools are<br />

not used to receive the spent fuel. The fuel is instead stored under dry conditions before being<br />

encapsulated.<br />

1.3.2 Deep repository<br />

<strong>SKB</strong>’s reference method for disposal of spent nuclear fuel is called the KBS-3 Method, where<br />

the abbreviation KBS stands for kärnbränslesäkerhet = Nuclear Fuel Safety. The method<br />

involves encapsulating the fuel in copper canisters which are then deposited, surrounded by<br />

a buffer of bentonite clay, in deposition holes in a tunnel system at a depth of approximately<br />

400–700 metres in crystalline bedrock, see Figure 1-6.<br />

The purpose of the three barriers (canister, buffer and rock) is to isolate the radionuclides in the<br />

fuel from the surrounding environment. Only if the radionuclides are brought up to the surface<br />

by the moving groundwater do they become harmful to man and the environment. In the deep<br />

repository it is primarily the canister that provides the isolating function. If radionuclides should<br />

escape from a leaky canister, their transport must be retarded. All barriers contribute to the<br />

retarding function. A partially damaged copper canister can effectively contribute to retardation<br />

by impeding inflow and outflow of water. The bentonite buffer has the capacity to retain many<br />

of the long-lived radionuclides, since they adhere to the surfaces of the clay particles. The rock<br />

contributes to the retardation by virtue of the low water flux at such great depth. Furthermore,<br />

radionuclides can adhere to fracture surfaces or penetrate into microfractures containing<br />

stagnant water.<br />

Cladding tube<br />

Spent nuclear fuel<br />

Bentonite clay<br />

Surface portion of deep repository<br />

500 m<br />

Fuel pellet of<br />

uranium dioxide<br />

Copper canister<br />

with cast iron insert<br />

Crystalline bedrock<br />

Underground portion of<br />

deep repository<br />

Figure 1-6. The KBS-3 method is based on multiple barriers (canister, buffer and rock) that<br />

prevent the radionuclides in the fuel from harming man and the environment.<br />

26 RD&D-<strong>Programme</strong> <strong>2004</strong>

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