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EIR-270.txt
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EIR-270.txt
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EIR-Bericht Nr. 270
EIR-Bericht Nr. 270
Eidg. Institut far Reaktorforschung Wirenlingen
Schweiz
The transmutation of fission products (Cs-137, Sr-90) in
a liquid fuelled fast fission reactor with thermal column
M. Taube, J. Ligou, K.H. Bucher
l I
B
Wilrenlingen, Februar 1975
EIR-Bericht Nr. 270
The transmutation of fission products (Cs-137, Sr-90) in
a liquld fuelled fast fission reactor with thermal column
M. Taube, J. Ligou, K.H. Bucher
February 1975
sSummary
The possibilities for the transmutation of caesium—-137
and strontium-90 in high-flux fast reactor with molten
plutonium chlorides and with thermal column 1s discussed.
The effecitve half 1life of Cs-137 could be decreased from
%0 years to 4-5 years, and for Sr-90 to 2-3 years.
Introduction
The problem of management of highly radiocactive fission product
waste has been intensely and extensively discussed in the recent
paper WASH - 1297 and especially in BNWL 1900 (Fig. 1).
Here only tne transmutation of Fission Products (F.P.) without the
recycling of the actinides 1s discussed, making use of neutron
irradiation by means of a fission reactor (Fig. 2).
A short outline of this paper 1s as follows
1) Why, contrary to many assertions, is neutron transmutation in
a fusion reactor not feasible.
2) Why recent discussions concerning transmutation in fission
reactors are rather pessimistic.
%3) Could the transmutation in a fission reactor be possible
taking into account the neutron balance in a breeding system?
1)y Which are the F.P. candidates for irradiation in a fission
reactor?
5) Is the rate of transmutation sufficiently high in a fission
reactor?
6) In what type of fission reactor is the transmutation physically
possible?
7) What are the limiting parameters for transmutation in a solid
fuelled fission reactor?
8) Is a very high flux fission reactor possible if the fuel is
in the liquid state instead of the solid state?
9) How could such a high flux fast reactor with circulating liquid
fuel and a thermal column operate as a 'burner' for some F.P.
(Cs-137 Sr~90 etc) transmutation.’
10) What engineering problems must be solved for this to be realised?
Radiocactive
Waste
— .
nigh active
low active
waste vaste
/N
any management
A
(ferbiaden
direct
controlled
storage on
tihe surface
litosphere
inydrosphere
{underground)
salt
rocks water ice
mines (deep sheet
see (polar)
floor
stable geologic
conditions nonstable
conditiocns
c
norn controlled
storage
solar deep
impact ¢
management dissipation
transnutation
without witn
cnanging changing
L and 4 A
{but no Z)
coculomb
exitation
(r,v) {(n,2n)
continously
with
cnanging
-
(p,Y)
periodical
fission
.
underground
xplosion
csmic
escape
neutrons neutrons
(primary) (secondary)
fusion fission accelerator
reactor reactor
A /\
fast thermal thermal fast
neutron reutron
with without
thermal tnermail
column column
(p,spallation)
thermonuclear
urcerground
slosion
Fig. 2
10
10
Transmutations of fission products
gquasi stable
F.P,.
Half-1ife, years
1074
stable
nuclides [Living
\E.P. . D,
r__\
\Gpontaneouse
beta decay
\
\
sShort
10
long 1L
i
10~
/
/
10
Cransmuta
iving
10
1. Why the transmutation of F.P., is not feasible in a controlled
thermonuclear reactor (CTR):
The recent studies of the use of a C.T.R. as a transmutation
machine for at least the conversion of Cs-137 have been to some
extent optimistic. Table 1 gives a summary of the most important
data and results from BNWL 1900.
Comments 1
Wolkenhauer (BNWL 4232) calculated the values with a nominal
one energy group cross sectlon and fast neutron {lux
5 X lOl5n cmdgs—l. (The primary flux of 14 MeV neutrons for
10 MW/m2 wall loading equals 5 x 101un cm—zs_l, but such a high
loading 1s very optimistic!)
Cs-137 Sr-90
o{barns) 2 O(S—l) o(barns) 7+ o(s H
(ngY) 0.44 2.0 loulo 0.0188 0.94 - 10-10
(n,2n) 0.147 7.3 - 1070 0.148 7.40 - 107 %Y
(g~-decay) - 8 25. 10 %Y _ 763 1710
The results obtalned are rather pessimistic since the values of
the reduction of the steady state amount due to the trans-
formations are given Dby:
. ~-10
for Cs-137 Atofal 17.76°10 - 2.15
Adecay g 06, 10—10
Atotal 15 97.10‘1O
for Sr-90 —_— = - = 2.09
rdecay 7.63'10—10
rtotal = Adecay + g« 9
Table 1 Transmutation possibilities for different devices (from BNWL-1900, WASH=-1297)
r
Machine Flux/ Reactions, and remarks of authors See
Energy of original reports. Comments
Accelerator of Protons Reaction (p,xn.) Not promising. Ruled out _
medium and high 100 MeV on basis of energy balance criteria
energy protons
Protons Spalation (p,xn) and (n,2n) {(n,vy)
1-10 GeV with secondary neutron flux
Cs=137 as Not feasible within limits of current -
target and/or technology. The capital cost 1is
thermalised prohibitive.
fflux of
neutrons
Fusion
(thermonuclear)
reactor in all
cases with wall
Fast flux of
Neutron reactions (n 2n) and &n,y)
Fast Flux of 5 x 10 5n cm~ s
14 MeV neutrons 2
from. (D-T) @ =
5x107 'n cm'ZS_l
Thermalised Practically only (n,y)
flux in Thermal flux 6.7 x 1015n em— 2t 2
beryllium trap
Attractive transmutation rate has not been
demonstrated but possible to transmutate 3
all Cs-137 and Sr-90 created by fission
reactors
Nuclear Fissile Technically not feasible. No. of explosions
explosions explosive or per year very high. Appr. 3900 p.a. each of
thermonuclear 100 k ton. (For USA in year 2000 Cs-137 and| —
explosive Sr-90) Probably not acceptable to public!
Fission See table 2
reactor
and are clearly too small for justifying such a complicated
technology as transmutation in a CTR. In spite of this Wolken-
hauer writes: "the flux level is somewhat higher than that
usually associated with CTR power plants. This value was selec-
ted based upon the hope that by the time transmutation 1s applied
in a CTR that technology will have advanced far enough to allow
for the implied vacuum wall lcocading. If this high a value proves
to be unrealistic longer irradiation times will be required"
"attractive transmutation rates have not been demon-
strated up to this point".
Also all these calculations were done on the basis of isotopically
pure Cs-137 and Sr-90. Later Wolkenhauer writes, "any practical
scheme would probably involve elemental rather than isotopic
loadings"
Comment 2
In BNWL-1900 it was noted that the calculation (in a moderating
blanket of the CTR) represents a more realistic blanket configu-
ration with a neutron wall loading of 10 MW/mz. (This is still
a very optimistic value. M.T.)
In this case the following date have been obtalned for a therma-
lised neutron flux from a CTR w1th a 10 MW/m wall locading.
¢ thermal ¢.0 .o total
n.cm_2s_l (n,vy) (n,2n) tl1/2 eff.
for 807% 6.71-1015 I ):0.117 (n.2n) 20,104 {a=22.2°10 ts7t
fraction > (barn) (barn)
- -10
~291 kg 7.91-10 U 7.0-10 1 9.9 years
Cs/yr
The conclusions of fthis study are that useful quantities of
Cs=137 could be transmuted under the projected CTR blanket
loading conditions. The reduction in Cs-137 "toxdicity" 1s still
expected to be at most a factor 3 down. In addition a study
of the bulld-up of fission product nuclei in order to establish
the requirements of periodic chemical processing and associated
costs has not been carried out.
Comment 3
H.W. Lefevre (appendix to BNWL-1900) makes an interesting comment
on the study of the transmutation of Cs-137 and Sr-90 in CTR:
'Everyone knows that a CTR will be "clean". Don't spoil that
illusion. I think that I would worry some about a CTR loaded
with 50 kg of Cs-13%7"'.
2. Why recent remarks about transmutations in a fission reactor
are rather pessimistic
A recent and most intensive study of the use of a fission reactor
for the transmutation of fission products has been published by
Claiborne (1972). He writes:
"The problem fission products cannot be eliminated by any system
of fission power reactors operating in elther a stagnant or
expanding nuclear power economy since the production rate exceeds
the elimination rate by burnout and decay. Only a equilibrium
will the production and removal rates be equal, a condition
that 1s never attalned in power reactors. Equilibrium can be
obtained, however, for a system that includes the stockpile of
fission products as part of the system inventory since the stock-
pile will grow until its decay rate equals the net production rate
of the system. For the projected nuclear power economy, however,
this will require a very large stockpile with 1ts associated
potential for release of large quantitites of hazardous radio-
isotopes to the environment. It is this stockpile that must
be greatly reduced or eliminated from the blosphere. A method
suggested by Steinberg et al. is transmutation in "burner reactors”,
which are designed to maximize neutron absorption in separated
fission products charged to a reactor. If sufficlent numberes of
these burners are used, the fisslon products inventory of a
nuclear power system can then reach equilibrium and be maintained
at an irreducible minimum, which is the quantity contained 1in the
reactors, the chemical processing plants, the transportation
system, and in some industrial plants.
If the assumption is made that burner reactors are a desirable
adjunct to a nuclear economy, what are the design requirements
and limitations: It 1s obvious that they must maximize (with
due regard to economics) the ratio of burnout of a particular
fission product to 1its production rate in fission reactors, and
the neutron flux must be high enocugh to cause a significant
decrease in its effective half-life. Of the fission types, the
breeder reactor has the most efficient neutron economy and in
principle would make the most efficient burner if all or
part of the fertile material can be replaced by a Sr-Cs mixture
without'causing chemical processing problems or too large a
perturbation in the flux spectrum because of the different
characteristics of these fission products. The cost accounting
in such a system would set the value of neutrons absorbed in
the fission product feed at an accounting cost equal to the value
of the fuel bred from those neutrons.
The maximum possible burnout of fission products would occur when
the excess neutrons per fission that would be absorbed in a
fertile material are absorbed instead in the fission product feed.
The largest possible burnout ratio would then be the breeding
ratio (or conversion ratio for non-breeders) divided by the
fisslon product yield. The estimated breeding ratio for the
Molten Salt Breeder Reactor (MSBR), a thermal breeder, is 1.05
and for the Liquid Metal Fuelled Fast Breeder Reactor (LMFBR),
1.38. The yield of 13705 + 9OSr is 0.12 atom/fission, but a number
of other isotopes of these elements are produced which would also
absorb neutrons. However, 1f the fission product waste is aged
two years before separation of the cesium and strontium, the
mixture will essentially be composed of about 80% 137Cs + 908r
and 207% 155 136Cs that
decays with a 13-day half-1ife (M.T. see Comment 4): consequently
137CS 950
+ Sr will be decreased by
Cs (which will capture neutrons to form
the maximum burnout ratioc for
20%. This leads to a maximum possible burnout ratio of about 7
for the MSBR and about 9 for the LMFBR. Unfortunately, however,
the neutron fluxes 1n these designs are well below lOl6n cm_zs_l.
Any modiflications of these designs to create high neutron fluxes
will increase the neutron leakage and decrease the burnout ratios
significantly." (Claiborne 1972)
10
Comment 4
It is not clear why Claiborne claimed that after 2 years ageing
and separation of strontium and caesium the isotope composition
will be
Cs=1357
807 Sr-90
20% Cs-13%5
From Crouch (1973%) the fission products of U-23%% have the following
composition (2 years ageing) (in at % per fissioned nucleous)
(see Table 3).
Sr-88 (stable) 3,63
Sr-90 (28 years) 4,39
Cs-1%% (stable) 6.57
Cs-134 (2 years) 3.5 (7.09+0.5 from independent yield)
Cs-135 6.26
Cs-137 5.99
Subtotal 30, 34
"he realistic data are unfortunately more than twice those cited
by Clalborne.
The same negative opinions concerning the use of Fission Reactors
for F.P.-transmutation are given by the following authors:
- A.S. Kubo (BNWL - 1900):
"Fission products are not conductive to nuclear transformation
as a general solution to long term waste management'.
- BNWL - 1900, itself:
"In summary it is improbable that transmutation of fission
products in fission reactors could meet any of the technical
feasibility requirements for the production of stable daughters'.
- Claliborne (1972):
"Developing special burner reactors with the required neutron
flux of the order of 1017n em™¢s™1 is beyond the limits of
current technology'.
5.
11
Is the transmutation in a fissilon reactor possible taking into
account the neutron balance in a breeding system?
In spite of all these pessimiétic opinions on the transmutation of
F.P. (especilally Cs-13%7 and Sr-90) in a fissilon reactor the dis-
cussion below points to a more optimistic conclusion.
The calculation of the transmutations of F.P. nuclides 18 made on
the basis of the following more or less arbitrary assumptions:
1)
The total number of fission power reactors installed must form
a self sustaining system (a breeding system) with a compound
doubling time TS of about 30 years (at a later date in the
development of cur civilization this may be satisfied).
T . 2.75 - M - (1L + ) . 1y D
5 (BR-1) + (1 + a) C
TS = compound doubling time (years)
M = 1initial fuel loading (kg/MW th)
C = fraction of time that reactor is at full power
F = ratio of the fertile isotope fission rate
o = capture to fission ratio for the fissile material
BR = breeding ratio
From this BR = 1 + exf2 * M (L + F) r 1In?2
We have postulated:
TS = 30 years
and we know that the mean values for 'our reactor' are
I3 = 0.20 (instead of 0.3, see Beynon 1974)
a = 0.24
M = 1 kg Pu/MWth
C = 0.8
and we obtain
2)
if
12
We know that the breeding ratio can be defined as
(v=1-a) + (F(v'-1)) - (A+L+T)
BR =
(L + a)
v and v' = number of neutrons per fission
A = ratio of parasitic capture rate in structural material
to fission 1n fissile material
T = ratio of parasitic capture rate in transmutated F.P.
to fission in fissile material
L = leakage ratio
In this paper the following rather For illustration only
conservative data are postulated (ref. Beynon, 1974)
GCFR LMFBR MSBR
L = 0.06 0.05 0.04 0.0244
A = 0.30 (instead of 0.23) 0.0067 0.09 0.163%
v = 2.96 2.95 2.93
vi = 2.70 2.92 2.77
F = 0.20 (instead of 0.30) 0.25 0.19
o = 0.24 0.22 0.28
we obtain
T = v-1-x-BR (1+x)-A-L + F (v'-1)
T = 0.364
T = 0 T=0 T =0 T = 0
then BR max. = 1.371 1.47 1.21 1.06
Table 2
Possibility for transmutation of F.P. - particularly
Sr-90 in a fission reactor according to BNWL - 1900
Cs=-13%7 and
Reactor
Reference
Flux
Remarks
thermal
power reactor
Steinberg
Wotzak
Manowitz,l1964
The authors use a wrong value:
Kr-85 with large 83 = 15 Dbarns
instead of 65 = 1.7 barns.
Isotopic separation of Kr-
isotopes
13
310 thermal
Only I-129 can be transmuted.
high flux (trap)
Steinberg, 1964
1016 in the trap
smaller 1n the
presence of the
F.P. target
An equal or greater no., of F.P.
would be formed in the fission
process per transmutation
event.
Claiborne, 1972
15
2+10 thermal
This reactor does not meet the
criteria of overall waste ba-
lance and of total transmuta-
tion rate.
ffast
ligquid metal
fast breeder
Claiborne, 1972
15
1-10 fast
Neutron excess 0.15 - 0.3 at
the expense of being no longer
a viable breeder of fissile
material. Also this flux does
not allow the attainment of a
sufficiently high transmutation
rate and is, therefore, not a
feasible concept.
fast with
thermal
Liguid fuel
fast reactor
with thermal
column
this paper.
¢T
14
The result can be checked as focllows:
In a mixed breeder/burner system let the ratio of the power be X
Breeder reactors power
Burner reactors power
From this
X-BR = (X + 1) BR
max in
also
BR = BR . + i
max min 1l + a
T
£ (Blen 1l + a) B Blen
_ 1+ a
X = BRmin T = 3,607
Conclusions
BR_ .
min
Tt is clear that a breeding-self transmutating system with
T >>0 1is possible only for a fast reactor in which the value of
breeding ratio BR is >1.3 and not for a thermal reactor in which
BR <1.06 (see Fig. 3).
15
Fig. 3 Burning of F.P. 1in steady state
Sr—=90 Cs-137
beta decay only
1
B tnermal
1074
Q) —
¢,
O
)
©
C
per ic recharging, 1 year
5 ,
0 10 ™
2
o
3
Q0 -
=
@
Q
o
43
s -
—
O
£ -3 . .
10 74 contlnouse reprocessing
i dwelling time: 10 days
16
4. Which fission products are candidates for transmutation?
In our case the amount of transmutatable nuclide can equal
T = 0.307
The tables of (BNWL-1900) provide the data for Fig. 4 in which
the radiloactivity of a I'.P. after a very short 'cooling' time
is seen, from which it is clear that the main hazard arises from
only a few radionuclides.
But these radionuclides nevertheless constitute the global
hazard even taking the amounts produced during the next period
of nuclear energy development.
The crucilal nuclides are characterised in Table 3 together with
other 1isctopes. All this data now makes i1t possible to estimate
the number of candidates for transmutation in our breeder/
burner system. The criterilia are as follows
- the total amount of all transmutated nuclides cannot be
bigger than the estimated value of T = 0.367, that is
~3%6 atoms of F.P. nuclides for each 100 fissioned
nuclides.
- fthe priority of transmutation is given as follows
Cs>Sr>I>Te>Kr Total equals: T = 0.3318
- in the first instance no isotopic separation process is
postulated.
Table % shows the F.P. nuclides selected for transmutation.
(see also Fig. 4).
Table 3 The priority for the transmutation of fissioned products
Selected Yield for fission of Atom/100 atom Pu-239 Assuming isotopic
100 atoms of Pu-239 Subtotal separation
atoms/100 atoms
Pu-239
Cs=-13%3% (stable) 6.91 6.91 0.14
Cs=-13%5 7.54 21.140 14.450 7.54 14,37
Cs-137 6.69 ' 21.140 6.69
Sr-90 2.18 25.32 2.18
Sr-88 (stable) 1.44x0.02 = 0.029 2.203 23,349 0.029 2.209
(2% isotopic
separation
efficiency)
I-129 1.17 } 24,519 1.17
I-127 (stable) 0.38 1.55 24,899 0.01 J 1-1°
Te-99 5,81 5.81 30.709 5.81 5.81
Kr-83% (stable) 0.36 h
Kr-84 (stable) 0.56
Kr-85 0.672 2. 14Th 0.67
0.
Krf86 (stable) 0.882 ) 3%.183 0.04 rt
Total 3%.18% 24,28
LT
curie/watt
Aectivity
18
1 day
]
10 days
100 days 1 year 10 years 100 years 1000 y.
i
| | | 1 1
time, seconds
19
5. Is the rate of transmutation good enough?
1t 1s clear that the rate of radiocactive nuclide removal in a
field of particles is given by:
ln 2
eff Adecay ¥ Atransmutation (s l) =
t 1/2 (eff)
where
A = g @
trans trans
. 2 ) .
o = c¢ross section (ecm ) for a given reaction
¢ = flux of the reacting particles (cmngs_l)
Let us assume that the energy production 1s based on a set of n
burners and nX breeders (see §3). At time tn (see Fig. 5) when
1t 1s declded to stop fission energy production in favour of
other sources the total amount of a selected fission product is
(1) (k) = (X + Ln<
el
with K = YP/E
Y = yield of the selected F.P.
P = power per burner (or breeder) (watt)
E = energy per fission (Joule)
This amount of F.P. 1s located only in the burners, therefore,
each burner can receive (X + 1)%eff although their own produc-
tion should represent only T in the steady state.
elfl
At time tn the nX breeders are shut down and only n burners are
in operation. Later on (time tn_l) the nuclide removal 1s
such that a rearrangement 1is possible and one burner can be
stopped, 1ts F.P. content will be loaded in the remaining burners
etc. At the beginning of each time step, tp, the p burners which
0c
A Fig. 5
(X + 1) V- . K - ,
\\ oo = 75 amount of F.P. produced by one burner
(n,1)(X+1) \\ eff in steady state
N\
N
\\
AN
X+1 \
p( ) \
N
N\
3(X+1)
\
N\
\\
2(X+1 '
( ) N
N
I N
N
(X+1) N
\\
1.2 T~
1.0 4 — 4+ e 5 — e e —
11 D DL 5 o N 0
Burner
number n n.l? P 3 2 = O
%EESS;P X-n 0 0 0 0 0 0
21
are stl1ll working contain the max. possible amount of F.P.:
where N(t) represents the total amount of the selected F.P.
One could imagine other schemes: for example one could make the re-
arrangement only when 2 burners can be shutdown. From the reacti-
vity point of view this solution is worse than the proposed one.
Coming back to the original proposal one has still to solve at
each time step (tp, tp_l) the burn up equation.
(3) ai Keff N = K.p where the right hand side is the F.P.
at production
Then the solution is
(4) N(t) = 22+ (e ) -
using (2) one deduces the time needed to go from p burners to
(p-1).
(5) Agrp (tp—l ~ tp) = 1ln
with a summation one gets the time t, after which one burner only
1
is 1in operation
(6) A
(b = &)