22.812 Nuclear Energy Economics and Policy Analysis S’04 Classnote

Th e Economic s o f th e Nuclea r Fue l Cycle : (2 ) MO X Recycl e i n LWRs

We can use the same fuel cycle cost model to investigate the economics of recycling plutonium in mixed-oxide fuel for LWRs.

The original expectation with regard to the plutonium in spent LWR fuel is that it would be extracted in reprocessing and then fabricated into mixed oxide fuel for fast breeder reactors. For a variety of reasons (mainly economic), the deployment of breeder reactors is not now expected to occur for many decades, at the earliest.

The only practical alternative use of plutonium in the short run is in MOX fuel for LWRs. Utilities in several countries are currently engaged in LWR MOX recycle.

But MOX recycle has been strongly opposed by environmental and non - proliferation advocates.

The question we will analyze is an economic one: Unde r wha t circumstances woul d i t b e economicall y attractiv e fo r a utilit y t o us e MO X fue l a s a n alternative t o lo w enriche d uraniu m (LEU ) i n LWRs?

To determine this, consider two utilities: Utility C the ‘conventional’ utility operating its PWR on the standard once-through fuel cycle, and utility E the ‘entrepreneurial’ utility contemplating a switch to the MOX cycle.

The two alternative fuel cycles are as follows:

UO X fue l cycl e (conventiona l once-through)

Enr

Ore

Disposal

Interim Storage

PWR

Fabric.

Tails

Disposal

Interim Storage

PWR

Fabric.

Pu

MOX

HLW+ILW

/LLW

Disposal

Spent OT fuel

Reprocess

-ing

MO X cycl e :

Nat U

Uranium credit

Utilit y C would be indifferent to either:

(a) arranging for storage and disposal of spent fuel or,

(b) surrendering the fuel to Utility E along with a payment that it would otherwise make for SF storage and disposal

In the latter case, Utility E could credit its operation with this payment, which would partly offset its costs of reprocessing, waste disposal, MOX fabrication, etc.

Utility E would be interested in proceeding with the MOX option if the total fuel cycle cost for the MOX fuel was competitive with the once-through fuel cycle cost.

Mak e th e followin g assumptions:

1. The contents of the spent fuel discharged from reactors operating on the UOX once-through cycle with a burnup of 50,000 MWDth/MTIHM are as follows:

Uranium: 93.4 w/o (U 235 enrichment: 1.1 w/o)

Plutonium: 1.33 w/o (total fissile enrichment (Pu 239 +Pu 241 ) = 0.93 w/o) Fission products: 5.15 w/o

Minor actinides: 0.12 w/o

(From Mcode results presented in Zhiwen Xu thesis)

2. Fissile plutonium (Pu 239 +Pu 241 ) is approximately equivalent to U-235 on a gram for gram basis; that is, equal weight percent enrichments of U-235 and fissile plutonium in U-238 are needed to drive a fuel assembly to the same cycle and discharge burnups. (In practice, MOX fuel has a lower initial reactivity for the same weight percent fissile enrichment, but undergoes a slower loss of reactivity with burnup.)

3. Value of uranium recovered from reprocessing spent PWR fuel is zero. (The recovered uranium is still slightly enriched in U-235, but other U isotopes make it less attractive, and under current market conditions, with low natural uranium prices, it is not economic to reuse it.)

4. MO X Fue l Cycl e Cos t Parameters

Transaction

Uni t Cost

Lea d Time (to start of MOX fuel loading)

Credit for elimination of SF interim storage and disposal cost

$500/kg HM

2 years

Reprocessing

$400 - $1600/kg HM

2 years

Uranium credit

0

--

HLW/ILW/LLW storage and final disposal cost

$200-400/kg HM in SF

1 year

Natural uranium ore purchase and yellowcake conversion

$40/kg HM

1 year

Blending + MOX fuel fabrication

$1500/kg HM

1 year

Interim storage of spent MOX fuel

$100/kg HM

At discharge

Final disposal of spent MOX $400/kg HM At discharge fuel

Note : Duration of irradiation = 4.5 years.

Q: How many kilograms of spent PWR fuel must be reprocessed and natural U purchased to produce 1 kg of MOX fuel at 4.51% fissile enrichment?

Let W be the mass of spent fuel (in kg/kg of MOX fuel)

Let M be the mass of natural uranium (in kg/kg of MOX fuel) Let x be the enrichment of fissile Pu in the MOX fuel

Let y be the enrichment of U-235 in the MOX fuel

M kg natural uranium

MOX

Fabrication

0.711 w/o U-235

Spen t fuel W kg HM

z kg fissile Pu

Reprocessing

fissil e Pu

1% loss 1% loss

of HM of HM

1 kg HM (as MOX)

x kg fissile Pu

y kg U-235

For fissile enrichment of 4.5%, we require

x + y = 0.0451 (1)

A material balance on the MOX fabrication stage for U-238 gives: M x 0.9929 x 0.99 = 1- 0.0451 = 0.9549

Thus,

M = 0.97 1 k g na t U

Material balance on the MOX fabrication stage for U-235 gives M x 0.00711 x 0.99 = y

Thus,

x = 0.00683 kg

Hence, from (1), y = 0.0383

Then, an overall material balance on fissile Pu gives z x 0.99 x 0.99 = 0.0383

Thus z = 0.0391 kg

And since the enrichment of fissile Pu in the spent PWR fuel is 0.93 w/o, we have that

W = 0.0391/0.0093 = 4. 2 kg

Thus, to produce 1 kg HM of MOX fuel we need to reprocess 4.2 kg HM of UOX SF and also purchase 0.97 kg of natural U.

Calculatio n o f MO X Fue l Cycl e Cost (Basis: 1kg MOX Fuel)

We use the approximate fuel cycle cost model for a single batch derived previously:

Total batch cost M i C i M i C i T i

i i

Transaction

SF Storage Disposal Credit

Reprocessing HL/IL/LL

Waste

Disposal

U purchase + conversion

MOX fab

Interim storage and disposal of MOX fuel

TOTAL

GRAND TOTAL

Unit Cost, C i ($/kg)

400

1000

300

40

1500

500

Mass Flow, T I (years) Direct Cost, Carrying M I (kg) M I C I ($/kg) Charge,

M I C I T I ( - 0.1/yr)

4.2 4.25 -2100 -893

4.2 4.25 4200 1785

4.2 3.25 1260 410

0.97 3.25 39 11.7

1.01 3.25 1515 492

1.0 -2.25 500 -113

5414 1692.7

$7107/kg HM MOX fuel

i.e. , MOX fuel cycle cost ~ 3 x once through cycle cost

= 7107 ($/kg U) x 1000 (kg/MT) x 1/50,000 (MTHM/MWD) x 1/24

(days/hr) x 1/ 1000 (MW/kw) x 1/0.33 (kwh(th)/kwh(e))

= 1. 8 cents/kwh(e)

If, in spite of this increased cost, all PWR UOX fuel was reprocessed and the Pu recycled, the incremental MOX fuel cost would contribute to an increase in the cost of electricity in proportion to the ratio of MOX to UOX fuel in the entire fleet. Accordingly, the incremental electricity cost for the fleet would be:

0.58 x (4.2/5.2) + 1.8 x (1/5.2) = 0.8 1 cent s pe r kwh(e) Questions

1. What is the minimum price of natural uranium ore at which MOX recycle would be economic?

2. What is the maximum cost of reprocessing at which MOX recycle would be economic?

3. Why are countries such as France and Japan pursuing MOX recycle?

Questio n 1

How high would the cost of uranium ore have to rise for MOX recycle to be economical?

1. Once through fuel cycle cost = 1691 + (10.45 c u + 10.45 x 4.25 x 0.1 x c u )

= 1691 + 14.9 c u

2. MOX cycle cost = 7056 + (0.97 c u + 0.97 x 0.1 x 3.25 x c u ) = 7056 + 1.29 c u Equating the two:

13.6 c u = 5365

c u = ~ 395 $/kg

(i.e., 10 x the current price of uranium!)

Questio n 2

How low would the cost of reprocessing go in order for MOX recycle to be economical?

1. Once-through fuel cycle cost = $2287/kg

2. MOX recycle cost = $1122 + 5.99 c R

Hence, even if reprocessing were free , the MOX cycle would not be economical! A different way to look at it:

Equating the once through and MOX cycle cost per kg:

1691 + 14.9 c u = 1071 + 5.99c R + 1.29c u

c u = 0.44 c R + 45.6

Breakeven uranium price as a function of reprocessing cost

2000

1800

Breakeven uranium price ($/kg U)

1600

1400

1200

1000

800

600

400

200

0

0 500 1000 1500 2000 2500 3000

Reprocessing cost ($/kg HM)

Questio n 3 wh y reprocess?

There are several reasons for this:

the lack of storage space for spent fuel

other environmental concerns

the belief that MOX recycle can contribute to energy security

the inertia associated with plans and contracts for reprocessing made decades ago.

NOTE: For a very detailed analysis of the issues discussed in this note, see Matthew Bunn et al, “The Economics of Reprocessing vs. the Direct Disposal of Spent Fuel”, Project on Managing the Atom, Kennedy School of Government, Harvard University, December 2003.