Euradwaste '08 - EU Bookshop - Europa
Euradwaste '08 - EU Bookshop - Europa Euradwaste '08 - EU Bookshop - Europa
disposal facility and decommissioning costs of the repository. The following costs are not included: R&D costs, nuclear regulatory costs, land lease/acquisition and real estate taxes. By definition, the costs related to interim storage of spent fuel are excluded. Table 2: Total estimated costs (Million Euro) of spent fuel disposal from Olkiluoto and Loviisa units (December 2006) Construction 630 above ground facilities 150 repository (incl. ONKALO) 480 Operation 2,140 encapsulation plant 1,120 canisters 530 repository 470 transports 20 Decommissioning and sealing 240 dismantling & waste management 10 repository closure and sealing 230 Total 3,010 3.3 Impact of parameters The results of cost estimate calculations for spent fuel are dependent on input parameters, some of which are based on the technical boundary conditions and some on economical and financial assumptions. The impact of parameters must be considered separately for the encapsulation process and underground disposal process. The crucial technical boundary conditions are obvious: quantity and burnup of spent fuel. The impact of quantity is straightforward as far as the capacity of encapsulation plant and underground repository is sufficient. There might be a case where a stepwise increase in a process becomes necessary, whereupon a corresponding stepwise rise in the costs will occur. Increasing burnup of spent fuel will increase the residual heat, which means either longer cooling times or larger disposal rock volumes. In practice, an optimisation will be made between these two factors. Prolongation of cooling times is feasible as long as the NPPs are operating but the situation changes once all units have been shut down. Scheduling of disposal activities is not only an economic issue, as it is dependent on the progress of the whole waste management programme, including policy decisions. A right timing of disposal activities facilitates an efficient use of encapsulation capacity. Many other factors may be considered, such as optimisation of resources in the whole disposal chain. There are many other technical parameters that affect the disposal costs: detailed design of the disposal concept, canister manufacturing process, rock excavation methods, tunnel backfilling process. In our case, there are two alternatives for the KBS-3 concept – vertical or horizontal location of the disposal holes (Fig. 1) – which possibly differ in costs. We consider at least three manufacturing processes for the copper canister: pierce and draw, extrusion, forging. Their unit costs are different but the final selection will be based on a combination of criteria. Our reference excavation method is drill and blast, but if for some reason another method must be used cost increase is to be ex- 52
pected. As to tunnel backfilling, there are many factors to be considered: backfill material, fabrication of backfill blocks, installation of backfill. We have now proceeded to an outline planning stage of the technical implementation of our repository. It is absolutely necessary to compile a data base of the relevant cost drivers and estimate the implementation costs of different alternatives simultaneously with design process. Also it is important to collect and analyse the realised costs. In our case, we have the unique possibility to receive cost information during the ongoing construction of ONKALO facility. Economical and financial parameters are typically outside our control. These include the price of raw materials, inflation, interest rate and return on investment. The essential raw material in our concept is copper. Latest observations demonstrate that its price is fluctuating rapidly and substantially. In these circumstances it is very difficult to predict the price of copper even at the moment when the disposal starts, not to mention the whole operating period of 100 years. The impact of inflation, interest rate and return on investment varies depending on the funding scheme. In our case, the return on investment of the State Fund is bound to market interest rate. In practice this means that profit of the Fund is dependent on the real interest rate. The impact of parameter variations in the range of the total costs of 3,000 Million Euro is illustrated in Table 3 for our concept and prerequisites. Relatively minor changes in parameters may cause a change of the order of 100 Million Euro in the total costs. Table 3: Impact of variation of different parameters in the total estimated costs (December 2007) Parameter Change in parameter Impact Amount of spent fuel 1 tU ~ 0.5 million Euro Burnup of spent fuel 5 MWd/KgU 7–8 years cooling time Operating time of disposal 1 year ~ 10 million Euro facility Price of copper 1 euro/kg ~ 35 million Euro Real interest rate 1 %-point ~ 20 million Euro 3.4 Evolution of cost estimates Spent fuel disposal costs have been estimated since the very beginning of the Finnish spent fuel management programme. First calculations were made in the early 1980s, and they have been updated regularly. There have been notable changes in the cost estimates based on the quantity of spent fuel, timing of disposal and development in disposal technology. The first estimate was based on the disposal of spent fuel from two Olkiluoto units. The next ones considered two Olkiluoto and two Loviisa units with relatively short design operating life times (40 years). The newest calculations include Olkiluoto 3 and extended life times (50-60 years). The new unit has an important effect in the operating time of the disposal facility, as the disposal of its spent fuel can start more that 40 years later than the disposal of fuel from the old units. 53
- Page 18 and 19: supported. The Commission believes
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- Page 22 and 23: Dr Bruno of Amphos 21 urged the swi
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- Page 28 and 29: Future directions There seemed to b
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- Page 51 and 52: Figure 3: Schematic diagram of the
- Page 53 and 54: contributed to enhance knowledge ab
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- Page 57 and 58: PANEL DISCUSSION Summary of the Pan
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- Page 65 and 66: collected in the cost of the nuclea
- Page 67: erated by Fortum) and one PWR unit
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- Page 79 and 80: Cooperation in the development of g
- Page 81 and 82: During the 1980’s it was realized
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- Page 88 and 89: Discussion: The chairman opened the
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pected. As to tunnel backfilling, there are many factors to be considered: backfill material, fabrication<br />
of backfill blocks, installation of backfill.<br />
We have now proceeded to an outline planning stage of the technical implementation of our repository.<br />
It is absolutely necessary to compile a data base of the relevant cost drivers and estimate<br />
the implementation costs of different alternatives simultaneously with design process. Also it is important<br />
to collect and analyse the realised costs. In our case, we have the unique possibility to receive<br />
cost information during the ongoing construction of ONKALO facility.<br />
Economical and financial parameters are typically outside our control. These include the price of<br />
raw materials, inflation, interest rate and return on investment.<br />
The essential raw material in our concept is copper. Latest observations demonstrate that its price is<br />
fluctuating rapidly and substantially. In these circumstances it is very difficult to predict the price of<br />
copper even at the moment when the disposal starts, not to mention the whole operating period of<br />
100 years.<br />
The impact of inflation, interest rate and return on investment varies depending on the funding<br />
scheme. In our case, the return on investment of the State Fund is bound to market interest rate. In<br />
practice this means that profit of the Fund is dependent on the real interest rate.<br />
The impact of parameter variations in the range of the total costs of 3,000 Million Euro is illustrated<br />
in Table 3 for our concept and prerequisites. Relatively minor changes in parameters may cause a<br />
change of the order of 100 Million Euro in the total costs.<br />
Table 3: Impact of variation of different parameters in the total estimated costs (December 2007)<br />
Parameter Change in parameter Impact<br />
Amount of spent fuel 1 tU ~ 0.5 million Euro<br />
Burnup of spent fuel 5 MWd/KgU 7–8 years cooling time<br />
Operating time of disposal 1 year ~ 10 million Euro<br />
facility<br />
Price of copper 1 euro/kg ~ 35 million Euro<br />
Real interest rate 1 %-point ~ 20 million Euro<br />
3.4 Evolution of cost estimates<br />
Spent fuel disposal costs have been estimated since the very beginning of the Finnish spent fuel<br />
management programme. First calculations were made in the early 1980s, and they have been updated<br />
regularly. There have been notable changes in the cost estimates based on the quantity of<br />
spent fuel, timing of disposal and development in disposal technology.<br />
The first estimate was based on the disposal of spent fuel from two Olkiluoto units. The next ones<br />
considered two Olkiluoto and two Loviisa units with relatively short design operating life times (40<br />
years). The newest calculations include Olkiluoto 3 and extended life times (50-60 years). The new<br />
unit has an important effect in the operating time of the disposal facility, as the disposal of its spent<br />
fuel can start more that 40 years later than the disposal of fuel from the old units.<br />
53