Development of a method for the estimation of low amountof plutonium in 200 L waste drums in presence of high amountof b c activity due to 137Cs and 60Co
Sarbjit Singh • Veena Sagar • Amol Mhatre
Received: 23 October 2012 / Published online: 17 November 2012
� Akademiai Kiado, Budapest, Hungary 2012
Abstract The waste drum monitoring system based on
HPGe detector was used to study its performance for the
estimation of low amounts of plutonium in presence of
high activity of 137Cs and 60Co. The counting was carried
out by keeping amount of plutonium constant at 100 mg
level and varying the count rate for the c rays of 137Cs and60Co. Present study has shown that the estimation of low
amount of 239Pu in a waste drum can be carried out using
129 keV c ray in the presence of 137Cs up to an activity
level of 16 mCi and in the presence of 60Co up to an
activity level of 8 mCi.
Keywords Waste drum monitoring � c Ray scanning
system � Plutonium � 239Pu � 240Pu � 241Pu � a Active waste �HPGe detector � 60Co � 137Cs � Dead time correction
Introduction
The quantitative assay of plutonium in the waste produced
during its handling is essential for nuclear material
accounting as well as for the assessment of radiological
hazards. The allowed limit for disposal of a active waste as
specified by I.A.E.A. [1] is 4,000 Bq/g which is equivalent
to *87 mg of 239Pu in a waste drum of 50 kg. Therefore
each drum has to be monitored for its a activity so that it
can be classified according to this limit. The a active waste
produced in a reprocessing plant may contain high b cactivity due to the presence of long lived isotope such as137Cs. Also some of the a active waste drums were found to
contain 60Co. The high count rate due to 137Cs and 60Co
increases dead time of the system and introduces a pile-up
effect which makes it difficult to estimate plutonium
amount in presence of 137Cs and 60Co. In our earlier
experiments, the performance of the system was studied [2]
for the estimation of plutonium at 4 and 1 g level in
presence of high b c activity of 137Cs. The work was
extended for estimation of *100 mg of Pu, the amount
closer to the allowed limit as specified by I.A.E.A. Sys-
tematic studies were carried out for plutonium estimation
in the presence of high b c activity of 137Cs and 60Co and
the results obtained are reported in the present work.
Experimental
Segmented c ray scanning system using a 20 % HPGe
detector system was set up [3] for the detection and estima-
tion of radionuclides present in 200 L waste drum. The
estimation of 239Pu was carried out using 129.3, 203.5, 375.0
and 413.7 keV c rays. The amounts of 240Pu (160.3 keV) and241Pu (237U) (148.6, 208.0 and 332.4 keV) were estimated
using their respective c rays.
Estimation of plutonium in presence of high b c activity
of 137Cs
The estimation of mg amount of plutonium requires
counting of drums for a long time due to very low abun-
dances of plutonium c rays. Hence, the conditions were
simulated for the presence of 97 mg of plutonium in 200 L
waste drum by keeping a suitable standard source of
S. Singh (&) � A. Mhatre
Radiochemistry Division, Bhabha Atomic Research Centre,
Mumbai 400085, India
e-mail: [email protected]
V. Sagar
Radioanalytical Chemistry Division, Bhabha Atomic Research
Centre, Mumbai 400085, India
123
J Radioanal Nucl Chem (2013) 297:149–152
DOI 10.1007/s10967-012-2322-9
plutonium near the detector. Since the actual handling of
the drums with high b c activity of 137Cs is difficult in the
laboratory, therefore counting was carried out by simulat-
ing the conditions for the presence of high activity of 137Cs.
The amount of plutonium was kept constant at 97 mg
and the count rate of 661.7 keV c ray of 137Cs was varied
from 0 to 3,000 counts per second (CPS). Gamma ray
spectrum analysis was carried out using DSPG [4] program
so as to eliminate any manual bias in the detection of peaks
and calculation of their areas. Dead time correction [5] was
applied to arrive at the corrected count rate for all the crays.
Standard drum containing known amount of 137Cs was
prepared based on the random distribution studies [6]
carried out earlier. This drum was counted on the c ray
scanning system for the emission rates and attenuation
correction [3]. The count rate of 137Cs for the known
activity (20 lCi) was obtained after applying the appro-
priate corrections for the dead time and attenuation. The
count rate of this standard drum was used to calculate the
activity of 137Cs present in the waste drum.
Estimation of plutonium in presence of high b c activity
of 60Co
The c ray energies (1,173.2 and 1,332.5 keV) of 60Co are
higher as compared to the c ray energy (661.7 keV) of137Cs. Hence the effect on the c rays of plutonium due to
the Compton of 60Co c rays will be much more than due
to the c ray of 137Cs. This will make it further difficult to
estimate plutonium in the presence of high amount of 60Co.
As mentioned above in the case of studies with 137Cs,
conditions were simulated for the presence of 97 mg of
plutonium and high activity of 60Co in 200 L waste drum.
The count rate of 1,332 keV c ray of 60Co was varied from
0 to 850 CPS and amount of plutonium was kept constant.
Standard drum containing known amount of 60Co was
prepared based on the random distribution studies [6]
carried out earlier. This drum was counted in a similar
manner as in case of 137Cs. The count rate of 60Co for the
known activity (10 lCi) was obtained after applying the
appropriate corrections for the dead time and attenuation.
The count rate of this standard drum was used to determine
the activity of 60Co present in the unknown waste drum.
Results and discussion
Effect of 137Cs activity on the estimation of plutonium
The plot of count rates for the 129.3 keV c ray of 239Pu as a
function of 137Cs count rate is shown in Fig. 1 and the plot
of the deviations in the count rate of 129.3 keV c ray as a
function of 137Cs count rate is shown in Fig. 2.
The deviation in the count rate for the 129.3 keV c ray
was found to be \25 % up to 2,000 CPS of 137Cs. The
deviation was found to increase slowly as the count rate of137Cs was increasing and was becoming erratic beyond
2,000 CPS. This deviation is due to the increase in the total
count rate of 137Cs and also due to the slope of the back
scatter peak (*185 keV). However, 129.3 keV c ray peak
was found to be less affected as it does not lie on the back
scatter peak or Compton (*476 keV) of the 137Cs spec-
trum (Fig. 3).
The 203.5, 375.0 and 413.7 keV c ray peaks of 239Pu
could not be seen in presence of high count rate (CPS) of137Cs. This may be due to the reason that these peaks are
lying in between the back scatter peak and Compton peak
of 137Cs. Variation in the slope of the spectrum introduces
additional error in the calculation of the peak areas of these
c rays. The statistical deviation also increases due to the
increase in the count rate of 137Cs.
It was possible to determine the amount of 241Pu using
148.60 keV c ray up to 500 CPS of 137Cs, but the statistical
deviation was very large due to its low abundance and low
amount of 241Pu. The 160.31 keV c ray peak of 240Pu could
not be seen as it is near the back scatter peak of 137Cs.
Effect of 60Co activity on the estimation of plutonium
Figure 4 gives the count rates for 129.3 keV c ray of 239Pu
as a function of 60Co count rate. The 129.3 keV c ray was
seen up to 800 CPS for 1,332 keV c ray of 60Co. The
375.0 keV c ray of 239Pu was seen up to 600 CPS and
413.7 keV c ray of 239Pu was seen up to 100 CPS only. The
203.5 keV c ray of 239Pu was not seen above 50 CPS of60Co. Also 160.3 keV c ray of 240Pu and 148.6 keV c ray
and 208.0 keV c ray of 241Pu were not seen above 50 CPS
of 60Co.
Fig. 1 Plot of the count rates for 129.3 keV c rays of plutonium as a
function of 137Cs count rate
150 J Radioanal Nucl Chem (2013) 297:149–152
123
Plot of the deviations in the count rate of 129.3 keV cray as a function of 60Co count rate is shown in Fig. 5.
Deviation in the count rate of 129.3 keV c ray was found to
be \15 % up to 600 CPS for the 1,332 keV c ray of 60Co.
Deviation in the count rate of 375 keV c ray was found to
be \30 % up to 600 CPS of 60Co whereas for 413 keV c
ray it was found to be \10 % up to 100 CPS of 60Co. The
deviation was found to increase slowly as the count rate of60Co was increasing beyond 100 CPS.
Gamma ray spectrum of plutonium in presence of
varying count rates of 1,332 keV c ray of 60Co is shown in
Fig. 6. The deviation observed in the count rate of pluto-
nium c rays is due to the increase in the Compton and back
scatter peak (*209 keV) of 60Co. However, 129.3 keV cray peak was found to be less affected as it does not lie on
the back scatter peak or Compton of the 60Co spectrum as
seen in Fig. 6.
The 203.5 keV c ray of 239Pu could not be seen in
presence of high count rate of 60Co because it is very close
to the back scatter peak of 60Co. The 375.0 and 413.7 keV
c rays of 239Pu could not be seen in presence of high count
rate of 60Co because these peaks are lying in between the
back scatter peak and Compton peak of the 60Co.
It was observed that 800 CPS of 60Co corresponds to an
activity of 8 mCi present in a 200 L drum. The 375.0 and
413.7 keV c rays of 239Pu have not been found suitable
when the amount of plutonium is small. However, the
estimation can still be carried out using 129.3 keV c ray of239Pu with 40 % variation up to 8 mCi of 60Co at 100 mg
level.
Comparison of results for the estimation of plutonium
with varying CPS of 137Cs and 60Co
Table 1 shows the comparison of results for % variation in
the count rates for c rays of 239Pu with varying CPS of137Cs and 60Co activity. Beyond these count rate limits of137Cs or 60Co, the deviations in the count rates for c rays of
plutonium isotopes were found to increase. It was observed
[2] that during studies on the estimation of plutonium in
presence of 137Cs, the deviations at 4 and 1 g level were
lower than that at 100 mg level. Variation in the count rate
was found to increase for higher count rate of 137Cs and
Fig. 2 Plot of the deviations in the count rate of 129.3 keV c rays of
plutonium as a function of 137Cs count rate
200 400 600 800 1000 1200 14000.0
5.0x105
1.0x106
1.5x106 2052 CPS66
1.7
keV
of C
s-13
7
413
keV
375
keV
Com
pton
edg
e
1141 CPS
498 CPS
0.1 CPS
0.1 498 1141
239Pu = 91 mg
2052
Bac
k S
catt
er P
eak
208
keV
203
keV
413
keV
375
keV
129
keV
129
keV
129
keV
Co
un
ts p
er c
han
nel
Channel number
Fig. 3 Gamma ray spectrum of plutonium (*0.1 g) in presence of
varying count rates of 661.7 keV c ray of 137Cs
Fig. 4 Plot of the count rates for c rays of plutonium as a function of60Co count rate
Fig. 5 Plot of the deviations in the count rate of c rays of plutonium
as a function of 60Co count rate
J Radioanal Nucl Chem (2013) 297:149–152 151
123
with decrease in the amount of plutonium. It was observed
that 375.0 and 413.7 keV c rays are more affected as
compared to 129.3 keV c ray of 239Pu. Moreover 203.5,
375.0 and 413.7 keV gamma peaks of 239Pu were much
more affected at 100 mg level as compared to gram level.
The 375.0 and 413.7 keV c rays of 239Pu have not been
found suitable when the amount of plutonium is very small.
However, the estimation can still be carried out using
129.3 keV c ray of 239Pu with 25 % variation up to 16 mCi
of 137Cs at 100 mg level. The limit for the estimation of
plutonium in the presence of 60Co is low, which is because
of the high Compton and back scatter peak of 60Co. Further
studies are planned for the improvements in the results.
Conclusions
Present study has shown that the estimation of 239Pu (gram
level) [2] can be carried out in the presence of high amount
of 137Cs up to an activity level of 20 mCi with a variation
of ±10 % and up to an activity level of 40 mCi with a
variation of ±15 %. However, the estimation of 239Pu at
100 mg level can still be carried out using 129.3 keV c ray
of 239Pu with 25 % variation up to an activity level 16 mCi
of 137Cs. The estimation of 239Pu up to 100 mg level in the
presence of 60Co can be carried out using 129.3 keV c ray
of 239Pu with 40 % variation up to 8 mCi level of 60Co.
The detection limit in the presence of high b c activity may
improve if the amount of 239Pu is more.
Acknowledgments We are thankful to Dr. A. Goswami, Head,
Radiochemistry Division for the encouragement in carrying out this
work. We are also thankful to Equipment Electronics Services Section
of Radiochemistry Division for maintenance of the HPGe detector
system.
References
1. IAEA (1994) Classification of radioactive waste: a safety guide,
safety series no. 111-G-1.1. International Atomic Energy Agency,
Vienna, p 13
2. Singh S, Mhatre A, Sagar V (2012) J Radioanal Nucl Chem
294(1):7–11
3. Singh S, Sagar V, Mhatre A, Ramaswami A (2006) Report BARC/
2006/I/015. Bhabha Atomic Research Centre, Mumbai
4. Rattan SS, Madan VK (1994) Report BARC/1994/E/038. Bhabha
Atomic Research Centre, Mumbai
5. Singh S, Mhatre A (2009) DAE–BRNS symposium on nuclear and
radiochemistry, NUCAR-2009. Chemistry Department, SVKM’s
Mithibai College of Arts, Mumbai, 7–10 January 2009, p A1
6. Singh S, Mhatre A (2009) DAE–BRNS symposium on nuclear and
radiochemistry, NUCAR-2009. Chemistry Department, SVKM’s
Mithibai College of Arts, Mumbai, 7–10 January 2009, p E1
0 500 1000 1500 2000 2500 3000
Channel number
Co
mp
ton
ed
ge
Co
mp
ton
ed
ge
Bac
k sc
atte
r
1332
( 60 C
o)
1173
( 60 C
o)
59.5
4 ( 2
41A
m)
28 192 296 471 741
0.0
2.0x105
4.0x105
6.0x105
8.0x105
1.0x106
1.2x106
Cou
nts
per
chan
nel
Fig. 6 Gamma ray spectrum of plutonium in presence of different
count rates of 1,332 keV c ray of 60Co
Table 1 Comparison of % variation in the count rates for c rays of
plutonium with varying CPS of 137Cs or 60Co
c, keV
(nuclide)
97 mg of plutonium 97 mg of plutonium
CPS of137Cs
%
Variation
CPS of60Co
%
Variation
129.3 (239Pu) 2,000 \25 600 \15
203.5 (239Pu) [50 Not seen
375.0 (239Pu) 500 \25 600 \30
413.7 (239Pu) [200 Not seen 100 \10
148.60 (241Pu) [50 Not seen
160.31 (240Pu) [50 Not seen
152 J Radioanal Nucl Chem (2013) 297:149–152
123