Science and Technology of Nuclear Installations

Volume 2012 (2012), Article ID 293467, 10 pages

doi:10.1155/2012/293467

Research Article

Economic Analysis of Different Nuclear Fuel Cycle Options

Won Il Ko and Fanxing Gao

Korea Atomic Energy Research Institute, Yuseong, Daejeon 305-353, Republic of Korea

Received 2 February 2012; Accepted 13 April 2012

Academic Editor: Katsuhisa Yamaguchi

Copyright © 2012 Won Il Ko and Fanxing Gao. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

An economic analysis has been performed to compare four nuclear fuel cycle options: a once-through cycle (OT), DUPIC recycling, thermal recycling using MOX fuel in a pressurized water reactor (PWR-MOX), and sodium fast reactor recycling employing pyroprocessing (Pyro-SFR). This comparison was made to suggest an economic competitive fuel cycle for the Republic of Korea. The fuel cycle cost (FCC) has been calculated based on the equilibrium material flows integrated with the unit cost of the fuel cycle components. The levelized fuel cycle costs (LFCC) have been derived in terms of mills/kWh for a fair comparison among the FCCs, and the results are as follows: OT 7.35 mills/kWh, DUPIC 9.06 mills/kWh, PUREX-MOX 8.94 mills/kWh, and Pyro-SFR 7.70 mills/kWh. Due to unavoidable uncertainties, a cost range has been applied to each unit cost, and an uncertainty study has been performed accordingly. A sensitivity analysis has also been carried out to obtain the break-even uranium price (215$/kgU) for the Pyro-SFR against the OT, which demonstrates that the deployment of the Pyro-SFR may be economical in the foreseeable future. The influence of pyrotechniques on the LFCC has also been studied to determine at which level the potential advantages of Pyro-SFR can be realized.

1. Introduction

Economics is an essential criterion to be considered in the future deployment of nuclear power. Today, the cost of electricity from nuclear power plants is, in most cases, highly competitive with other electricity-producing means, and is generally lower in cost than fossil fuel, wind, or solar energy. However, a closer look at nuclear power production brings an insight that the cost varies within a wide range, depending on the nuclear fuel cycle option. With the current trend toward competition in the power market, the option of nuclear fuel cycle is an important determinant in terms of economics.

Four nuclear fuel cycle options can be considered in the foreseeable future under the nuclear power situation in the Republic of Korea: a once-through cycle (OT), DUPIC recycling (DUPIC), thermal recycling using MOX fuel in a PWR (PWR-MOX), and SFR recycling employing pyroprocessing (Pyro-SFR). A comprehensive comparison among the proposed fuel cycle options necessitates an economic analysis for each option based on the material flow estimation. The objective of this work is to provide a systematic cost comparison among these nuclear fuel cycles.

FCC includes a front-end cost and back-end cost as well as costs associated with fuel recycling in the cases of recycling options. An economic analysis of FCC is a subject of great interest, which not only concentrates on the cost differences among these four fuel cycle options but also efficiently avoids the large uncertainties of the Generation IV reactor capital costs.

The levelized cost is a fundamental calculation principle in the energy and power industry. It is particularly appropriate for an estimate of the costs of energy given the various technologies. LFCC has offered an effective indicator for an economic comparison among nuclear fuel cycles and was adopted to compare the four fuel cycle options considered in this study [1].

The material flow is the basis used to obtain the LFCC. There are mainly two models to calculate the material flows [2–5]. One is an equilibrium model, and the other is a dynamic model. The equilibrium model focuses on a batch study with the assumptions that the whole system is in a steady state and that the mass flow as well as electricity production throughout the fuel cycle is in an ideal equilibrium state, which calculates the material flow for the production of a certain amount of electricity to obtain the LFCC with reference to unit cost. The dynamic model takes the timing into consideration to simulate a relatively realistic case. The dynamic model offers a better way to simulate the complement process of a fuel cycle, which may take several decades. Comparatively, the equilibrium model enables a clear and direct comparison to suggest which optimized system should be complemented in the future. In particular, while the current research and development of certain technologies such as SFR and pyroprocessing are still underway, an equilibrium model offers a way to avoid large uncertainties of the future development and deployment. In this study, an equilibrium model was therefore built to calculate the material flow on a batch basis. With the unit costs being determined, the cost of each step of the fuel cycle could be obtained as an approach to obtain the LFCC.

The change of each key component due to the uncertainties can result in considerable differences in LFCCs among the fuel cycle scenarios. To take these unavoidable uncertainties into account, a wide range was applied to each unit cost, and the distribution of LFCC was obtained.

2. Reference Fuel Cycle and Material Flows

The four fuel cycle options considered in this study are specified by the breakdown structures consisting of a series of components (or steps), as shown in Figure 1. Figure 1(a) describes the OT material flow, which utilizes low-enriched uranium in a PWR without reprocessing of the spent fuels (SFs).

(a) once-through (OT) cycle

(b) dUPIC recycling

(c) PWR-MOX recycling

(d) Pyro-SFR recycling

Figure 1: Main components in the nuclear fuel cycles.

PWR SFs still contain fissile materials, approximately 0.9 w% U-235 and 0.5 w% Pu-239, depending on a 3.5% U-235 enrichment of the initial fuel and a burnup of 35 GWd/tHM, and therefore can be used as the fuel for CANDU reactors after the removal of some fission products (FPs). This PWR-CANDU symbiotic fuel cycle is referred to as DUPIC recycling [6], and the material flow is described in Figure 1(b).

Some Pu isotopes such as Pu-239 and Pu-241 are fissile, such as U-235, and can be burned using a thermal neutron spectrum. In the PWR-MOX option shown in Figure 1(c), a commercial PUREX technology is used for recovering U and Pu from the PWR SFs. The reprocessed materials can be fabricated into the mixed oxide (MOX) fuels of UO₂ and PuO₂ and then loaded into PWRs, while the MOX SFs would be permanently disposed of without further recycling.

A fast reactor utilizes fast neutrons of which a higher energy can burn both U-235 and transuranic elements (TRUs). This aspect makes it possible to transmute the TRUs and extract energy at the same time. In Pyro-SFR recycling shown in Figure 1(d), the PWR SFs are to be reprocessed to obtain TRU-bearing fuels for fast reactors, while the remaining uranium partitioned from the PWR SF would be disposed of as low- and intermediate-level radioactive waste. In this cycle, a sodium-cooled fast reactor (SFR) with a conversion ratio of 0.6067 is considered as the reference fast reactor [7]. Pyroprocessing has been developed to reprocess the oxide fuels discharged from PWRs and to fabricate metallic fuels containing TRU for future SFRs [8]. The metal fueled SFR using alloys of actinides zirconium (AcZr) has a high potential for recycling actinides by being integrated with the pyroprocessing. The TRU fuel after burning in the SFR would be repeatedly reprocessed through pyroprocessing, and the recovered TRUs would be recycled into an SFR to close the fuel cycle. However, it should be noted that practically some nasty TRU isotopes have to be separated and treated as HLW.

The material flow values in Figure 1 were calculated using the equilibrium model based on an output of 1 TWh of electricity, a detailed description of which refers to the previous material flow study [9].

3. Unit Cost Specification

The cost data in this paper are presented in 2010 US dollars. Cost data reported at different times were converted into the 2010 values using an escalation rate of 3% [10, 11]. It is difficult to estimate the absolute value of each of the components specified in Figure 1 because many uncertainties exist. Therefore, a range of unit cost (i.e., lower bound, nominal value, and upper bound) was applied in regard to these uncertainties. The nominal value refers to the best estimated unit cost. The lower bound means the low cost case, and the upper bound means the high cost case [5, 11]. It should be noted that the reactor capital and operating costs were not included in the FCC, which was calculated based on the premise introduced by the GEN IV program, in which the targets of the GEN IV reactor capital costs are to be comparable with those of the GEN III reactors [12]. It should be acknowledged that the capital cost taking around 80% of the total electricity cost [13]. Taking no account of the reactor capital cost, therefore, largely reduces the uncertainty of the SFR, and therefore enhances and emphasizes the contribution of the fuel cycle to the total electricity cost.

The main sources of the unit cost data used in this study were from an OECD/NEA study [1, 5, 11] and Advanced Fuel Cycle Cost Basis (short for AFCCB) [14–16], and engineering judgments were used when certain data were not available. The summarized data before converting to the 2010 values are listed in Table 1. Some specifications of the key components are described as follows. It should be noted that the cost difference of MOX fabrication for LWR is dramatically big between the OECD study and AFCCB study. For the OECD 2006 study [5], the cost is 1250$/kgHM. However, for the Advanced Fuel Cycle Cost Basis study, the cost is 3200$/kgHM [15]. The difference mainly lies in the technical readiness and the considerations on proliferation resistance (PR) as stated in the AFCCB reports. In our study, we admit the big gaps among different countries concerning the status of MOX fuel fabrication technique. In addition, the PR is definitely important for the future deployment of the fuel cycle, and therefore, the bigger unit cost from the US study was adopted.

Table 1: Unit costs for nuclear fuel cycle steps.

Cost items
Units
Low
Nominal
High

Uranium
$/kgU
30
158
354

Conversion
$/kgU
5
12
15

Enrichment
$/SWU*
80
155
180

Reprocessing

    PUREX
$/kgHM
700
800
900

    Pyro-UO₂
$/kgHM
500
1,500
2,500

Fuel fabrication

    UO₂ fuel
$/kgHM
200
240
300

    MOX fuel
$/kgHM
2,000
3,200
4,000

    DUPIC fuel
$/kgHM
500
700
900

Pyro. and SFR metal fuel fab.
$/kgHM
2,500
5,000
7,500

Long-term storage

    Depleted U
$/kgHM
2.6
3.6
4.6

    Reprocessed U
$/kgHM
2.6
3.6
40.0

Transport and storage

    DUPIC SF
$/kgHM
50
100
250

    UO₂ SF
$/kgHM
105
125
145

    MOX SF
$/kgHM
145
218
580

    Decay storage
$/kgHM
10,000
22,500
35,000

    HLW
$/m³
80,060
120,090
200,240

Disposal

    Packaging

        UO₂ SF
$/kg
100
200
350

        DUPIC SF
$/kg
80
150
250

        MOX SF
$/kg
200
400
700

        HLW of PUREX
$/m³
100,000
200,000
400,000

        HLW of others
$/m³
100,000
200,000
400,000

    Underground cost
$/m³
600
1,200
2,000

*SWU stands for separative work unit.

3.1. Uranium Price

The uranium cost generally takes around 40% of the NFCs. The nominal value of the natural uranium price (158$/kgU) was from the monthly average price of December 2010 [17]. The upper bound value of the uranium price was based on the spot price of the historical peak value of June 2007, as shown in Figure 2 [17], which was much higher than the reference data of OECD/NEA and AFCCB. It is challenging to project the future uranium price due to the complexity of the price determinants, such as supply and demand. The uranium price reported in AFCCB was higher than those published by OECD/NEA in 2006. AFCCB reported the uranium price to be a low cost of 50$/kgU, nominal cost of 100$/kgU, and high cost of 150$/kgU in April 2007 (based on the values at 2007), but in March 2008, it was reported as a low cost of 25$/kgU, nominal cost of 60$/kgU, and high cost of 240$/kgU (based on the values at 2007), respectively. However, these costs were changed into a low cost of 30$/kgU, nominal cost of 75$/kgU, and high cost of 260$/kgU in December 2009 based on the values of that year. It seems to be obvious that the newer reports suggest a wider range of uranium price.

Figure 2: Uranium spot prices.

It is reasonable to doubt the relatively lower prediction of the uranium price. However, the reason for the adoption of the peak value in this study is to enlarge the possible range of the uranium price to better reflect the high uncertainty of the future uranium price.

3.2. Conversion and Enrichment

The nominal price of conversion and the enrichment processes are from the monthly price of December of 2010. Low and high estimates are referred from the OECD/NEA report [5] and the AFCCB reports [14–16]. The high estimated cost of enrichment of OECD/NEA in 2000 is smaller than the spot price based on 2010, and thus an estimated value of 180$/SWU was proposed.

3.3. Pyrotechnique Cost

As no commercial experience exists, the unit costs concerning the pyrotechnique for fuel reprocessing are theoretical and estimated using engineering judgments with high uncertainty. Because of the difference of the fuels treated and a big gap between the material flows evolved, there are two pyrotechnique-related components in the Pyro-SFR recycling scenario. One pyrotechnique treats the PWR SF (named as Pyro-UO₂), which includes an additional electroreduction procedure to reduce the oxide fuels into the metallic fuels, and the other is used for SFR metallic SFs (named as Pyro-Metal-Fab.), which requires a fuel fabrication facility along with it. The unit costs reported in AFCCB 2008 [15] were applied to give a nominal cost of 5000$/kgHM for Pyro-Metal-Fab., and the unit cost of 1500$/kgHM is defined for Pyro-UO₂ with regard to the study at the Korea Atomic Energy Research Institute [6, 18]. As the R&D proceeds, more economical cost data might be expected.

3.4. Storage Cost

It is assumed that the interim storage cost consists of two parts: a fixed cost and a variable cost depending on the storage time, which was set for 5 years in this paper [1, 5]. The decay storage of Cs and Sr which are main heat emitters separated by pyroprocessing, employs a shallow disposal as a low-interim level waste for around 200–300 years [18].

4. Fuel Cycle Cost Calculation

4.1. Lead and Lag Time

The costs depend on the amount of material or service consumed and the unit price of each component. The payments for the various components of the nuclear fuel cycle are usually made at different moments in time. Each step-cost should be calculated with consideration of its implementation time, starting from the fuel purchase costs and ending to the final disposal costs. It is therefore reasonable to consider the discount rate to compare all the payments at the same time according to the refueling interval plus or minus a lead or lag time as listed in Table 3.

4.2. Electricity Generation

(1)the amount of fuel required by one reactor is estimated based on the reactor parameters, fuel loading per core (MTHM):

where , and are the electric power (MWe) of a reactor, the specific heat (MWt/MTHM), and efficiency (%), respectively;(2)the annual requirement of fuel (MTHM) is calculated based on fuel burnup and other parameters:

where and are the capacity factor (%) and burnup (MWD/MTHM), respectively;(3)the electric power generation (MWh) per fuel loading (MTHM) is calculated as follows:

The number of PWRs is determined from the equilibrium core ratio mentioned above.

4.3. Fuel Cycle Cost

The amount of fuel passing through a certain step multiplied with the unit cost of the specific material offers the fuel cost of a single step and combined with the additional cost associated with the operation, the overall cost of an operation, namely, the component cost, can be obtained. By summarizing the costs of all the operations involved in an NFC, the overall costs of the NFC can be obtained as listed in Table 3. The method employed for the calculation of FCC is the constant money (levelized life-time cost) method. The levelized unit cost is based on the cash flow of all component costs discounted to the base year. A 5% discount rate was applied to all unit costs in this paper. To get the total fuel cycle cost, the net present value (NPV) was used, which can be expressed as follows:

4.4. Levelized Fuel Cycle Cost

The LFCC is derived in terms of mills/kWh (1 mill equals to 10⁻³ $) by dividing the NPV of the entire fuel cycle cost by the NPV of the total electricity output over the plant life-time as follows:

where is the electric power generated.

4.5. Uncertainty Analysis

The unit costs for each of the components in the fuel cycle were applied using an uncertainty analysis by Monte Carlo simulation using Latin Hypercube extraction mode [19]. It was assumed that the costs of the components would be simulated by triangular distribution. The triangular distribution is a representative nonparametric distribution, which is effective in cases when there is not much data, and the distributions are unknown. The triangular distribution may appear symmetric, right-skewed, or left-skewed according to the expert opinions. The triangular distribution has a very obvious appeal because it is easy to think about the three defining parameters in a fuel cycle economic analysis and to envisage the effect of any changes.

4.6. Sensitivity Analysis

This study conducted a sensitivity analysis of some unit costs in which the variability is considered large, such as the uranium price, Pyro-UO₂ reprocessing, and Pyro-Metal-Fab. The break-even prices necessary for the Pyro-SFR fuel recycle to be economic compared to the OT option were also obtained by changing the input of the uranium price, Pyro-UO, and Pyro-Metal-Fab., respectively.

5. Results and Discussion

5.1. Levelized Cost of Electricity

The calculation results of the LFCC concerning these four fuel cycle scenarios show the following: OT 7.35 mills/kWh, DUPIC 9.06 mills/kWh, PUREX-MOX 8.94 mills/kWh, and Pyro-SFR 7.70 mills/kWh. The relative total costs of the fuel cycle options are presented by the bar chart in Figure 3. It shows that DUPIC, PWR-MOX, and Pyro-SFR are 23%, 22%, and 5% higher than the OT option, respectively.

Figure 3: Relative LFCC of four fuel cycles.

Figure 3 shows that the uranium price is the key cost component of the LFCC in all of these four nuclear fuel cycles. With the current uranium price, the OT is the most economical option and the Pyro-SFR is the second due to the low uranium consumption. In the Pyro-SFR scenario, the uranium consumption decreases because of the utilization of the metal fuel made from the reprocessed TRU. Pyro-Metal-Fab., however, makes up for the difference in uranium costs between the Pyro-SFR and OT scenarios. In the PWR-MOX scenario, the uranium consumption is still high, while meanwhile the reprocessing is costly. The relative high cost of the DUPIC scenario is because of the low uranium utilization efficiency due to the low burnup and high fabrication cost required to make the PWR SF into CANDU fuel.

Generally, two decisions, that is, which kind of reactor to employ and whether or not to deploy a spent fuel treatment technology, mainly determine the direction of the nuclear fuel cycle. In this study, we focused on the impact of the introduction of spent fuel treatment technologies, that is, PUREX, DUPIC, and pyroprocessing. The introduction of reprocessing techniques in PWR-MOX and Pyro-SFR scenario do affect the back-end cost due to the recycling of Pu or TRU. For the DUPIC case, the treatment of spent PWR fuel for CANDU fuel plays a similar role to take advantages of residual fissile in the spent fuel. Due to the introduction of techniques to treat the PWR spent fuel, the mass flows of nuclear fuel cycles were changed accordingly. Therefore, it is informative to present the cost share of the spent fuel treatment technique in the LFCC as shown in Figure 4.

Figure 4: Share of spent fuel treatment techniques in the LFCC.

5.2. Uncertainty Analysis

The results from the Monte Carlo simulation are shown in Table 4 and Figure 5. With the assumption that each unit cost has a triangular distribution, a total of 50,000 extractions of Latin Hypercube were performed. The standard deviation (SD) for the LFCC ranges between 1.16–1.69 mills/kWh, as shown in Table 4. The difference between the LFCC of the Pyro-SFR and OT is 0.04 mills/kWh concerning the mean data, which is much smaller than the SD for the OT option, 1.69 mills/kWh. This means that the cost of the Pyro-SFR fuel recycling lies within the error bound of the direct disposal option. The costs of DUPIC and PWR-MOX also have the possibility to fall within the error bound of the OT, respectively, but their possibilities are relatively smaller.

Figure 5: Comparison of the probabilistic density function of LFCCs using a triangular distribution.

5.3. Sensitivity Analysis

A sensitivity analysis was conducted on the key cost components, such as the uranium price, Pyro-UO₂, and Pyro-Metal-Fab. Figure 6 shows the results of regression sensitivity analysis, for which a multivariate stepwise regression was applied as an analytical method for the sensitivity of multiple inputs and for deriving the regression coefficient to assess the degree of sensitivity. A value of 1 of the regression sensitivity means that a variation of 1 SD for the input variable brings a variation of 1 SD in the results. On the contrary, a regression sensitivity of 0 means that there is no influence from the input to the output.

(a)

(b)

(c)

(d)

Figure 6: Sensitivity coefficient of fuel cycle components.

As can be noted from Figure 6, the uranium price indicates the highest sensitivity value. It was determined that the regression coefficient of the uranium ranges from 0.95 to 0.96 for the OT, DUPIC, and PWR-MOX options. However, the coefficient of the Pyro-SFR fuel recycle, 0.85, shows a lower sensitivity of the uranium price compared to other fuel cycle options. While another high sensitivity factor is shown to be the uranium enrichment in the OT and PWR-MOX scenarios. In the Pyro-SFR option, Pyro-UO₂ and Pyro-Metal-Fab. show higher sensitivities.

5.4. Break-even Uranium Price

Since uranium is the main driver of the LFCC, a fluctuation of uranium price influences the total cost considerably. The historical data of uranium price, however, changed dramatically, and it is challenging to predict the future uranium price. A large range of uranium prices is therefore adopted to find out at which price level the recycled fuel cycle options will be more economical than the OT option, or at which level they will break even.

The sensitivity analysis on the uranium price shows that the OT option depends more on the cost of uranium than on any other fuel cycle options (Figure 6 and Figure 7), which could be explained by the largest amount of uranium consumed for producing a given quantity of energy. Pyro-SFR, however, is much less sensitive to the uranium price indicated by a smaller slope in Figure 7. By increasing the uranium price, the LFCC of the OT option finally reaches and surpasses those of Pyro-SFR and PWR-MOX, respectively, due to the different weight of uranium cost in each cycle scheme.

Figure 7: LFCCs dependent on the uranium price.

A break-even price is defined to specify the price at which the LFCC of the OT equals the LFCC of another fuel cycle option. The calculation of uranium break-even price is a kind of sensitive analysis. By setting the input unit costs fixed and only changing the uranium unit price, a unit price of uranium can be derived at which the LFCC cost of a specific nuclear fuel cycle equals to the LFCC of OT. However, it should be noted that the calculation was based on the reference unit cost listed in Table 2. Even the nominal data have unavoidably uncertainty and that is why a cost scale is associated with each unit cost. However, the nominal data is currently highly reliable, and the purpose of calculating the break-even price is to indicate a potential trend not to offer a precise and exact data, so the use of the nominal data for discount rate sensitive analysis is reasonable.

Table 2: Lead and lag time of fuel cycle steps.

Fuel cycle process
Lead/lag time (month)

Lead time (month)
Purchase
21

Conversion
18

Enrichment
12

Fabrication
6

Lag time (month)
Interim storage
18

Reprocessing
78

Final disposal
480

Table 3: Equations used in levelized fuel cycle cost calculation.

Cost of each fuel cycle component
Cost calculation methods

Uranium
,                                                 

,                                     

where

Conversion
,                                                 

where

Enrichment
,                                                 

where                             

Fabrication
,                                                     

where

Transport and storage
,                 

where

Disposal
,                                                  

where                                                     

Fx: Cost of fuel cycle component ($), Mx: Mass of materials (kg), fx: Loss factor (%), Px: Unit cost ($/unit), lx: Material loss (%), ex: Fraction of U-235 (%).

Subscript x: U: Natural uranium, C: Conversion, E: Enrichment, F: Fabrication, TS: Transportation & storage, D: Disposal, f: Feed natural uranium (0.71%), p: Product of uranium fuel, t: Tail.

Table 4: Results of a Monte Carlo simulation for the uncertainty analysis of LFCCs.

OT
DUPIC
PWR-MOX
Pyro-SFR

Min.
3.99
5.68
5.74
4.51

Max.
13.79
15.30
14.77
12.64

Mean
8.35
10.06
9.83
8.31

SD
1.69
1.57
1.55
1.16

The break-even price of uranium was calculated to be 800$/kgU for PWR-MOX fuel cycle and 215$/kgU for Pyro-SFR fuel cycle with reference to the OT option. The actual price of uranium in July 2007 recorded 350$/kgU, which is 13 times higher than that of 2001. If Pyro-SFR was available as of 2007 peak in uranium price, its nongeneration fuel cycle costs would have been competitive with those of the OT. The gap of LFCCs between the Pyro-SFR and OT still exists at the current uranium price. The amount of uranium with an acceptable price, however, is definitely decreasing, and the nuclear power capacity in East Asia is increasing dramatically at the same time. According to this trend, the higher uranium consumption efficiency a nuclear fuel cycle pursues the better competitiveness it may obtain.

5.5. Break-even Uranium Price Dependent on Pyrotechniques

With regard to a potential cost decrease of certain components, it is of great interest to analyze the influence of the changes of fuel cycle components on the LFCCs, especially focusing on the cost of Pyro-UO₂ and Pyro-metal-Fab., respectively.

Pyro-UO₂ and Pyro-Metal-Fab. are currently under development, and there is no industrial experience worldwide yet. The cost data concerning those unavoidably maintain a high uncertainty. Pyro-UO₂ and Pyro-Metal-Fab. contribute heavily to the LFCC of Pyro-SFR recycling by changing the cost of each pyrotechnique, and it is therefore possible to estimate the sensitivity of the break-even uranium price of the Pyro-UO2 and Pyro-metal-Fab. compared with OT, as shown in Figure 8. When the cost of Pyro-UO₂ equals to the cost of PUREX, or around 50% of the nominal unit cost, the break-even price of uranium is around 125$/kgU. This means when the cost of Pyro-UO₂ becomes equal to the cost of PUREX, the LFCC of Pyro-SFR cycle can become the same as the LFCC of the OT with a uranium price of 125$/kgU. If the unit cost of Pyro-Metal-Fab. decreases by 50% of the current nominal unit cost, the break-even price of uranium is around 110$/kgU by reaching which the LFCC of Pyro-SFR and LFCC of OT become the same value. The research and development of pyrotechniques may offer a promising economic advantage to Pyro-SFR over the others.

Figure 8: Break-even uranium price dependent on pyrotechniques.

5.6. Sensitivity Analysis of Pyro-UO₂ and Pyro-Metal-Fab

The sensitivity analysis was also performed on the key components of Pyro-SFR with comparatively high uncertainty at the current price. For instance, the reference unit cost of 1500$/kgHM for Pyro-UO₂ and 5000$/kgHM for Pyro-Metal-Fab., as quoted from the AFCCI report, was deemed to be a bit too high by some commentators, in view of the possible decrease by research and development.

The break-even price of Pyro-UO₂ with reference to the OT option was evaluated to be 920$/kgHM, which is around 61% of the nominal cost, as shown in Figure 9. This calculation was performed by varying the Pyro-UO₂ costs, while all other costs were fixed to their reference values until the equalization with that of the OT cost was achieved.

Figure 9: LFCC of Pyro-SFR dependent on the cost of pyrotechniques.

The break-even price of Pyro-Metal-Fab. was calculated to be 4422$/kgHM, which is around 88% of the nominal cost, as shown in Figure 9. This break-even price is 18 times higher than the nominal cost of uranium fuel fabrication, which indicates that a promising price decrease may be realized by research and development.

6. Conclusion

The economics of OT, DUPIC, PWR-MOX, and Pyro-SFR fuel cycle scenarios have been calculated and compared by employing an equilibrium model. LFCCs were obtained for a fair comparison: OT 7.35 mills/kWh, DUPIC 9.06 mills/kWh, PUREX-MOX 8.94 mills/kWh, and Pyro-SFR 7.70 mills/kWh. The uranium price in the four scenarios generally acts as the dominant driver of LFCCs. Pyrotechniques also weigh considerably in the Pyro-SFR scenario. In consideration of the current unavoidable uncertainties introduced by certain cost data, a cost range and the triangle techniques were used to perform an uncertainty study, which indicates that the gap between the Pyro-SFR and OT fuel cycle scenarios is relatively smaller than the other options.

Also, the sensitivities of uranium, Pyro-UO₂, and Pyro-Metal-Fab. were carried out to determine the potential advantages of the Pyro-SFR scenario. The break-even price of uranium for a Pyro-SFR was obtained by an increase in the uranium price within a large range, and the break-even price was 215$/kg for Pyro-SFR and 800$/kg for PWR-MOX. With regard to the uranium historical peak price in 2007, it may be worth deploying Pyro-SFR in the foreseeable future. The influences of pyrotechniques on the LFCC of the Pyro-SFR were carried out to clarify the targets for current immature technologies. If the current uranium price remains stable, the break-even price for Pyro-UO₂ is 920$/kgHM and 4422$/kgHM for Pyro-metal-Fab., respectively, which are actually close to the nominal costs employed.

In conclusion, the difference in the fuel cycle costs between the Pyro-SFR and OT fuel cycle is negligible, considering the uncertainty associated with the unit cost of the fuel cycle components. Therefore, other factors such as technological and political risks, environmental effects, public acceptability, and nonsproliferation, could play important roles in determining the future nuclear fuel cycle options.

Acknowledgments

This project has been carried out under the Nuclear R&D Program funded by the Ministry of Education, Science, and Technology of Korea.

References

OECD/NEA, The Economics of the Nuclear Fuel Cycle, OECD, Paris, France, 1994.

B. Dixon, W. Halsey, S. Kim, G. Matthern, S. Piet, and D. Shropshire, Dynamic Systems Analysis Report for Nuclear Fuel Recycle, INL/EXT-08-15201 Rev.1, 2008.

Economic Analysis Working Group. AFCI Economic Tools, Algorithms, and Methodology, INL/EXT-07-13293, 2009

J. M. Deutch and J. P. Holdren, The Future of Nuclear Power: An Interdisciplinary MIT Study, Massachusetts Institute of Technology, Cambridge, Mass, USA, 2003.

OECD/NEA, Advanced Nuclear Fuel Cycles and Radioactive Waste Management, NEA No. 5990, OECD, Paris, France, 2006.

W. I. Ko, J. W. Choi, J. S. Lee, H. S. Park, and K. J. Lee, “Uncertainty analysis in DUPIC fuel-cycle cost using a probabilistic simulation method,” Nuclear Technology, vol. 127, no. 1, pp. 123–140, 1999.

S. G. Hong, et al., “600 MWe sodium cooled fast reactor core designs for efficient TRU transmutation,” The Korean Nuclear Society Spring Meeting, Chuncheon, Korea, May 2006.

T. Inoue, “Actinide recycling by pyro-process with metal fuel FBR for future nuclear fuel cycle system,” Progress in Nuclear Energy, vol. 40, no. 3-4, pp. 547–554, 2002.

B. H. Park, F. Gao, E. H. Kwon, and W. I. Ko, “Comparative study of different nuclear fuel cycle options: quantitative analysis on material flow,” Energy Policy, vol. 39, no. 11, pp. 6916–6924, 2011.

M. Bunn, J. P. Holdren, S. Fetter, and B. Van Der Zwaan, “The economics of reprocessing versus direct disposal of spent nuclear fuel,” Nuclear Technology, vol. 150, no. 3, pp. 209–230, 2005.

OECD/NEA, Accelerator-Driven Systems (ADS) and Fast Reactors (FR) in Advanced Nuclear Fuel Cycles, OECD, Paris, France, 2002.

OECD, Cost Estimating Guidelines for Generation IV Nuclear Energy Systems, OECD, Paris, France, 2006.

OECD, Trends in the Nuclear Fuel Cycle: Economic, Environment and Social Aspects, OECD, Paris, France, 2000.

D. Shropshire, et al., Advanced Fuel Cycle Cost Basis, INL/EXT-07-12107, 2007.

D. Shropshire, et al., Advanced Fuel Cycle Cost Basis, INL/EXT-07-12107 Rev.1, 2008.

D. Shropshire, et al., Advanced Fuel Cycle Cost Basis, INL/EXT-07-12107 Rev.2, 2009.

The Ux Consulting Company, Weekly spot Ux U₃O₈ price, 2010, http://www.uxc.com/review/uxc_Prices.aspx

W. I. Ko, H. Choi, and M. S. Yang, “Economic analysis on direct use of spent pressurized water reactor fuel in candu reactors-IV: DUPIC fuel cycle cost,” Nuclear Technology, vol. 134, no. 2, pp. 167–186, 2001.

W. I. Ko, J. W. Choi, C. H. Kang, J. S. Lee, and K. J. Lee, “Nuclear fuel cycle cost analysis using a probabilistic simulation technique,” Annals of Nuclear Energy, vol. 25, no. 10, pp. 771–789, 1998.