Upload
ctbto
View
0
Download
0
Embed Size (px)
Citation preview
Isotopic Characterization of Radioiodine and Radioxenon in Releases from Underground
Nuclear Explosions with Various Degrees of Fractionation
MARTIN B. KALINOWSKI1 and YEN-YO LIAO
1
Abstract—Both radioxenon and radioiodine are possible indi-
cators for a nuclear explosion. Therefore, they will be, together with
other relevant radionuclides, globally monitored by the International
Monitoring System in order to verify compliance with the Com-
prehensive Nuclear-Test-Ban Treaty once the treaty has entered into
force. This paper studies the temporal development of radioxenon
and radioiodine activities with two different assumptions on frac-
tionation during the release from an underground test. In the first
case, only the noble gases are released, in the second case, radioio-
dine is released as well while the precursors remain underground. For
the second case, the simulated curves of activity ratios are compared
to prompt and delayed atmospheric radioactivity releases from
underground nuclear tests at Nevada as a function of the time of
atmospheric air sampling for concentration measurements of 135I,133I and 131I. In addition, the effect of both fractionation cases on the
isotopic activity ratios is shown in the four-isotope-plot (with 135Xe,133mXe, 133Xe and 131mXe) that can be utilized for distinguishing
nuclear explosion sources from civilian releases.
Key words: Nuclear explosion, test ban, CTBT, isotope
activity ratios, radioiodine, radioxenon, fractionation, radioactivity
monitoring, source discrimination.
1. Introduction
Due to their half-lives, fission yields and decay
radiation the iodine radionuclides 135I, 133I and 131I as
well as the xenon radionuclides 135Xe, 133mXe, 133Xe
and 131mXe are relevant for detecting a nuclear
explosion (DE GEER, 2001). Though two of the latter
are metastable isomers, for convenience, this paper
refers to the entities of this quartet as the four relevant
xenon isotopes.
Xenon isotopes are the most likely observable
radioactive signatures of underground nuclear
explosions because xenon is a gas and chemically
inert. Radioiodine is volatile and can also be released
from underground nuclear explosions. Since it is less
likely to escape from deep underground than xenon,
however. it is still much more likely to be released
than its particle bound precursors in the decay chains,
and some degree of fractionation can be expected.
This fractionation influences the temporal develop-
ment of the radioxenon isotopes released from
underground into an atmospheric plume, because it
depends on the amount of its radioiodine precursor
isotopes which are present in the same plume. This
paper studies empirically the degree of fractionation
and theoretically the impact of various fractionation
scenarios on the isotopic activity ratios of radioxenon.
Atmospheric radioiodine and radioxenon are
monitored on a daily basis at the radionuclide stations
(see, e.g., KALINOWSKI and SCHULZE, 2002) of the
International Monitoring System (IMS) that is cur-
rently being established (see, e.g., HOFFMANN et al.,
1999; KALINOWSKI 2006). Though it may be released
in gaseous form, during its transport through the
atmosphere iodine tends to undergo to some degree
chemical reactions and subsequently to attach itself to
aerosol particles. It will be collected on particle filters
at the 80 radionuclide stations of the IMS network.
For radioxenon, suitable sensors will be installed at
40 of these stations with the option of a later
expansion to all 80 sites of the radionuclide particle
monitoring network.
A previous paper described the temporal devel-
opment of prompt and delayed atmospheric
radioactivity releases from underground nuclear
tests at the Nevada Test Site in the United States
(KALINOWSKI, 2011). A subset of this data is used in
this paper to investigate the degree of fraction-
ation that occurred with the reported releases of
1 Carl Friedrich von Weizsacker Center for Science and
Peace Research (ZNF), Beim Schlump 83, 20144 Hamburg, Ger-
many. E-mail: [email protected]
Pure Appl. Geophys.
� 2012 Springer Basel AG
DOI 10.1007/s00024-012-0580-7 Pure and Applied Geophysics
radioiodine at that site. Other previous papers pre-
sented the proof of principle (KALINOWSKI and PISTNER,
2006) and a demonstration (KALINOWSKI et al., 2010)
of a robust method for discriminating between the
source being a nuclear explosion or a civilian reactor
source. The method is based on isotopic activity ratios
of radioxenon in the atmosphere. This paper builds on
those findings and explores the impact of various
fractionation scenarios on the radioxenon isotopic
activity ratios. A companion paper explores the
capability to use activity ratios of radioiodine iso-
topes for source characterization (KALINOWSKI et al.
2012).
In the first section of this paper, the simulations of
various nuclear explosion types and fractionation
scenarios are presented. The second section uses the
empirical release data of underground nuclear tests at
the Nevada Test Site to explore the degree of frac-
tionation by comparing their isotopic activity ratios
with those of the simulations. The third section shows
the effect of fractionation on the radioxenon isotopic
activity ratios for source discrimination.
2. Simulated Radioxenon Isotopic Activities Under
Different Fractionation Assumptions
A nuclear explosion takes place in a very short time
where the nuclear chain reaction and possibly fusion
reactions occur on a time scale of a few millionth of a
second and less. In this short instant, the initial feed of
hundreds of fission products is formed and radioactive
decay dictates the subsequent activity changes with
time. Three different scenarios are studied here with
regard to the combination of fissile material used and
the neutron energy spectrum. Fission of 235U and 239Pu
is simulated at fission neutron energies using the
Bateman equations (BATEMAN, 1910) implemented in
Matlab (KALINOWSKI and PISTNER 2006; LIAO, 2011).
The independent fission yields and the decay branch-
ing fractions are taken from ENGLAND and RIDER
(1994). These were adopted for ENDF/B-VI. Differ-
ences for figures in other libraries are most significant
for the short lived pre-cursors. One day after the fission
process ended, the uncertainty originating from the
library values is negligible for the purpose of this
paper.
The development over time for simulated
radioxenon and radioiodine isotopic activity ratios
with regard to different nuclear explosion scenarios
has been published before (KALINOWSKI, 2011). In the
totally unfractionated case, all fission products are
staying together, perhaps in an underground cav-
ity, such that in-growth from precursors is fully
allowed.
Fractionation changes the isotopic activity
ratios. The temporal development of radioiodine
activities with various fractionation scenarios after
a nuclear explosion is plotted in the companion
paper (KALINOWSKI et al., 2012). For radioxenon, two
different fractionation types are considered in this
paper. In the standard type, radioxenon is fully
removed from all its precursors immediately, or at a
later time, and from then on decays without further
in-growth from the decay chain. The alternative
fractionation type considered here assumes that ra-
dioxenon and radioiodine are fully removed from all
other precursors together and at the same time. The
different impacts of these two fractionation types on
the development over time of radioxenon activities
can be seen in Fig. 1 using 235U with fission energy
neutrons as example. The activity in TBq refers to a
1 kT explosion. The resulting curves for isotopic
activity ratios are presented together with data from
the Nevada Test Site in the following section.
As can be seen in Fig. 1, there is a strong impact
of fractionation that is most pronounced for early
separation of the volatiles from the non-volatile pre-
cursors. The unfractionated case is represented by the
upper curve while the simulated fractionations start at
various delay times (0.01, 0.1, 1, 10 and 100 h) from
that line and stay always below it. The impact gets
less with increased delay between time zero and the
separation time and eventually vanishes at a delay
time related to the relevant half-lives. The impact is
of course strongest for radioxenon separating from
the precursors alone and less pronounced for xenon
and iodine separating together. This can be noted in
Fig. 1b by the lower curves all bending upwards
before going down due to decay in contrast to Fig. 1a.
For 131mXe, the maximum activity can be reduced by
almost five orders of magnitude if separated alone
from all precursors and by more than three orders of
magnitude if iodine and xenon are separated together.
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.
However, the fractionation of iodine and xenon
together has no significant impact on the radioxenon
activities, if it happens later than 1 h after the
explosion. For xenon separating alone, the impact is
still strong after 10 h and for 131mXe even after
100 h.
Figure 1Different impacts of two fractionation types on the development over time of radioxenon activities using 235U with fission energy neutrons as
an example. a Radioxenon is removed from all precursors, b radioxenon and radioiodine are removed together. The activity in TBq refers to a
1 kT explosion
Isotopic Characterization of Radioiodine and Radioxenon
The parent of the isomer 131mXe, 131I, has a half-
life of 8.02 days. The other isotopes have shorter-
lived precursors with a maximum of 2.19 days
(133mXe) for 133Xe, 20.8 h (133I) for 133mXe and
6.61 h (135I) for 135Xe. Due to the long half-life of its
precursor, the presence of 131mXe in the set of
quantified isotopes provides a good capability for
distinguishing different types of sources by separat-
ing them in a multi-isotopic-ratio plot (KALINOWSKI
et al., 2010).
3. Empirical Radioiodine Release Data
of Underground Nuclear Tests
SCHOENGOLD et al. (1996) report detailed atmo-
spheric radioactivity release information for 433
nuclear tests conducted on the Nevada Test Site
(NTS) from 15 September 1961 through 23 Septem-
ber 1992. An analysis of these data can be found in
KALINOWSKI (2011). Only for 45 of the 433 releases,
two or more radioiodine isotopes were reported. 131I
and 133I were measured in all of them except for one
case each. Only in 24 of the 45 cases the third rele-
vant radioiodine isotope (135I) was measured.
Information for all these releases is collected in
Table 1. Both particulate and gaseous radioiodine
were measured and Table 1 gives the sum of the
activities collected on glass fiber filters and in char-
coal cartridges.
Twelve of the reported releases of radioiodine were
uncontrolled ventings following very quickly after the
explosion but with no more than 1 h delay. Five inci-
dents of measuring radioiodine resulted from cratering
explosions that set the material free without delay. In
six cases, these were operational releases.1 At least
38 h after the explosion and with passing the releases
through a particulate air and charcoal filter combina-
tion, a further 22 cases were operational releases
without filtering occurring between five and 312 h
after the explosion. The duration of uncontrolled
releases is very short, up to half an hour. For opera-
tional releases with filtering, the releases are reported
to last between 10 min and 114 h, without filtering
between 6 and 130 h.
For some tests, more data are available than
reported in SCHOENGOLD et al. (1996). For one of the
prominent examples, the Sedan test conducted on 7
June 1962, PLACAK (1963) contains atmospheric
concentrations observed at several stations. All 18
samples with two or three radioiodine isotopes mea-
sured in the charcoal cartridges are collected in
Table 2.
Measurement uncertainties are reported neither
in SCHOENGOLD et al. (1996) nor in PLACAK (1963)
but all data is given with two significant digits. The
largest uncertainty is related to the time for which
the reported values are valid. The passage of a
plume is often not matching the sampling periods
and uncertainties in fixing a time to which the
measurement is corrected bears uncertainties due
to the change of atmospheric concentrations during
plume passage.
For the operational releases, the sampling times
are identical to the release periods reported in
SCHOENGOLD et al. (1996). For the ventings and cra-
tering tests, the sampling times are different from the
reported release delay and duration. For these tests,
beginning and ending of gas sampling at the sites hit
by the radioactive cloud are gathered from the rele-
vant documents issued by USPHS (U. S. Public
Health Service) and EPA (Environmental Protection
Agency). With this information and the known time
of the explosion, the delay and duration of the sam-
pling period during which the cloud passed were
calculated. These times are plotted in Figs. 3, 4, 5
together with the associated radioiodine ratio values.
The length of the time bar marks the sampling
duration. The reported activity is normally extrapo-
lated to the middle of the sampling period and in a
few cases to the time of the cloud passage. Figure 2
demonstrates this for the example of the test called
Pampas as part of Operation Nougat conducted on 1
March 1962. The 9.5 kt charge was detonated at
11:10 PST. The Gunderson’s Ranch station began
sampling at 12:45 and ended at 17:50 at the same day
(USPHS, 1964). The delay of sampling start can be
calculated to be 2 h 35 min (marked with A in the
1 Operational releases result from purging of tunnels or
sometimes shafts to minimize the exposure to personnel, from drill-
back operations to recover samples for diagnostic purposes, from
gas sampling or from sealing the drill hole with a plug and
cementing it to the surface (SCHOENGOLD et al., 1996).
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.
Table 1
The table lists all historical releases of radioiodine from nuclear explosions at the Nevada Test Site between 1961 and 1992 as reported by
SCHOENGOLD et al. (1996)
Days Month Years Test name Depth (m) Delay of
sampling
start (h)
Sampling
duration (h)
I-131 (Ci) I-133 (Ci) I-135 (Ci) Type Yield
(kt)
15 9 1961 Antler 400 2.52 4.32 4.2 102 450 1 2.6
22 12 1961 Feather 250 7.79 0.79 – 27 94 1 0.15
1 3 1962 Pampas 360 4.125 2.54 0.012 0.29 0.47 1 9.5
5 3 1962 Danny Boy 34 2.542 2.46 73,000 290,000 470,000 4 0.43
14 4 1962 Platte 190 4.25 1.42 11.4 75 120 1 1.85
13 6 1962 Des Moines 200 2.25 2.92 33,000 38,0000 5,400,000 1 2.9
6 7 1962 Sedan 195 3.03 3.58 8,80,000 2,400,000 11,000,000 4 100
11 7 1962 Johnnie Boy 1 11.75 2 70,000 130,000 320,000 4 0.5
19 10 1962 Bandicoot 240 28.25 0.083 9,000 – 73,000 1 12.5
14 11 1963 Anchovy 260 24 6 2.5 11 350 3 Low
23 1 1964 Oconto 265 38 26 0.001 0.0005 – 2 10.5
13 3 1964 Pike 114 7.17 0 360 13,000 – 1 \20
19 8 1964 Alva 166 85 129.6 0.041 0.055 – 3 4.4
5 12 1964 Crepe 220 217.75 38.4 1 1 – 3 3.4
18 2 1965 Wishbone 179 20 216 1.3 15 26 3 \20
3 3 1965 Wagtail 750 168 6 0.03 0.02 – 3 20–200
20 3 1965 Suede 143 31.37 15.5 0.1 1.6 0.89 3 \20
26 3 1965 Cup 537 79.27 89 0.3 0.7 – 3 20–200
5 4 1965 Kestrel 447 112.58 16.5 0.029 0.09 0.00029 3 \20
14 4 1965 Palanquin 85 11.02 0 9,06,000 3,500,000 7100000 4 4.3
21 5 1965 Tweed 281 96.87 120 0.014 0.0068 – 3 \20
23 7 1965 Bronze 531 150.17 6 0.23 0.23 – 3 20–200
21 8 1965 Ticking 208 47.75 16.25 0.16 0.13 – 3 \20
27 8 1965 Centaur 172 45.5 1.5 0.0022 0.0065 – 3 \20
12 11 1965 Sepia 241 96 6 0.0011 0.0035 0.0001 3 \20
18 1 1966 Sienna 275 46.42 6 0.0016 0.0056 0.0002 3 \20
3 2 1966 Plaid II 270 52.5 74.4 0.019 0.076 – 3 \20
23 4 1966 Fenton 167 5.08 115.2 0.056 2.4 7.3 3 1.4
12 9 1966 Derringer 255 0.83 47.1 1.5 41 152 1 7.8
5 11 1966 Simms 198 48.33 47.7 0.009 0.018 – 3 \20
25 10 1967 Cognac 301 24 6 0.0049 0.027 0.003 3 \20
26 1 1968 Cabriolet 52 2.33 4.66 6,000 90,000 – 4 2.3
12 3 1968 Buggy a-e 41 1.55 5.13 22,000 200,000 970,000 1 5.4
27 8 1968 Diana Moon 242 5 13 0.1 2.1 3.6 1 \20
12 9 1969 Minute Steak 264 0.083 3.92 0.05 3.4 34 1 \20
18 12 1970 Baneberry 278 0.5 259 80,400 1,200,000 – 1 10
25 7 1972 Atarque 294 144 6 1.7E - 06 1.4E - 06 – 3 \20
9 8 1972 Cebolla 287 312 48 2.4E - 07 2.4E - 08 – 3 \20
25 4 1973 Velarde 277 48 6 0.027 0.14 0.016 3 \20
14 8 1974 Puye 430 168 6 2.1E - 06 8.6E - 07 2.5E - 09 2 \20
3 8 1983 Laban 326 48 0.8 0.000011 0.000025 – 2 \20
22 3 1986 Glencoe 610 120 6 8.9E - 06 9.6E - 06 – 3 29
21 5 1986 Panamint 480 55 0.0617 0.0001 0.0009 – 2 \20
13 5 1988 Schellbourne 463 56.9 113.5 0.000032 0.00011 – 2 20–150
10 3 1990 Metropolis 469 48 48 0.000088 0.00019 – 2 20–150
Only those tests are included for which at least two radioiodine isotopes were measured. The activities include both particulate and gaseous
radioiodine. A dash (–) means that the concentration was below the detection limit. The types of the releases are noted with the following
numbers: type 1 uncontrolled rapid venting, type 2 operational release with filtering, type 3 operational release without filtering, type 4
cratering
Isotopic Characterization of Radioiodine and Radioxenon
figure) after the explosion and the sampling duration
is 5 h 5 min (marked with B).2
4. Further Comparisons of Observed and Simulated
Data
The simulated radioiodine isotopic activity ratios
are compared to the values of reported releases from
nuclear tests at the Nevada Test Site. Figure 3 applies
for the ratio between 135I and 133I, Fig. 4 for 135I and131I and Fig. 5 for 133I and 131I. The data are picked
from SCHOENGOLD et al. (1996) to show all releases
from Nevada tests in the three plots labeled a) and
from PLACAK (1963) to show all data from the Sedan
test only in the three plots labeled b). The simulations
use 235U (a) and 239Pu (b) with fission energy neu-
trons and assume complete fractionation at various
time steps.
In each figure, the unfractionated case is repre-
sented by the lower curve while the simulated
fractionations start at various delay times (0.001,
0.01, 0.1, and 1 h) from that line and stay always
above it, except for some cases at separation times in
the order of minutes and shorter. The simulated
curves range over many orders of magnitude and
show the largest spread in the time frame between an
hour and a day after the explosion. However, the
dynamic range is dominated by early fractionations.
Obviously, a separation between radioiodine and its
precursors later than 1 h after the explosion has little
impact on the isotopic activity ratio and remains close
to the unfractionated case.
Most of these data in the plots of Figs. 3a, 4, 5a
(Nevada releases as reported by SCHOENGOLD et al.,
1996) lie at the lower end of the simulated curves
indicating either no fractionation of radioiodine from
its precursors at all or a fractionation later than 0.1 h
after the explosion. However, some data are found
outside the range of the theoretical curves, most of
them show a lower than expected isotopic activity
ratio. In general, the agreement of low lying data
points is better with the simulation for 239Pu and this
Table 2
The table lists all observations of radioiodine from the cratering nuclear explosion with a yield of 100 kt TNT equivalent that was called
Sedan and conducted at a depth of 1 5 m on 6 July 1962
Delay of sampling
start (h)
Sampling
duration (h)
Time activities
apply to (h)
I-131
(llCi/m3)
I-133
(llCi/m3)
I-135
(llCi/m3)
0 6.62 3.03 260 13,000 60,000
6.75 3.52 8.367 28 780 –
0 21.83 3.033 7.2 240 500
21.83 23.167 33.42 11 170 –
45 24 57 7.1 34 –
0 21.5 9.5 0.27 4.4 –
21 24.5 33.25 19 860 –
0 10 10 5.2 250 –
10 12 10 70 2,400 –
0 11 3.83 0.22 4.2 –
0 26.25 12.17 6.5 220 510
0 21 9 – 5.0 6.8
3.25 24 5.5 49 200 –
1.083 15.67 2.25 75 3,900 9,300
23.5 7.167 27.083 10 260 –
0 20 4.3 12 79 –
20 24 32 6.9 190 –
0.67 24 12.67 0.23 3.3
Only those measurements are included which are based on iodine collected on charcoal (gaseous fraction) and for which at least two
radioiodine isotopes were quantified as reported by PLACAK (1963). A dash (–) means that the concentration was below the detection limit
2 The data point used in Fig. 2 was deliberately selected to fit
well with the simulation in order to demonstrate how delay and
duration are graphically represented.
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.
is reasonable because most underground tests in
Nevada were dominated by plutonium fission. The
assumption of 235U being the fission material catches
a few data points that lie above the highest simulation
line for 239Pu. Only two single outliers on the high
end of activity ratios cannot be understood by the
simulations. For the test called ‘‘Anchovy’’ on 14
November 1963 at 8 o0clock local time, the 135I to133I activity ratio is as high as the simulation is only
within a few hours after the test explosion (see
Fig. 3a, highest data point at the 1-day delay line).
However, for the delay reported, it is one order of
magnitude higher than the case of instantaneous
fractionation immediately after the time of the
explosion. Even though the time of the release is not
reported by the hour, it definitely happened on the
calendar day after the test, i.e., with a 16-h delay for
the unrealistic assumption that the drill-back opera-
tion was conducted right at midnight. More likely, the
delay was 24 h. For the Puye test on 14 August 1974,
the activity ratio (see Fig. 3a, lowest data point at the
1-week delay line) could be understood, if the drill-
back took place 5 days after the test instead of the
reported delay of 7 days. Two further data have their
x mark (for the time the decay corrected concentra-
tion is valid) to the right of the simulation curves
while the respective sampling periods start left to the
curves, i.e., earlier. A possible explanation might be a
too large delay reported for the plume passage.
On the low end of activity ratios, the deviations of
reported data from the simulation curves cannot be
considered as spurious outliers and need to be
explained. The picture is less serious for the 135I to133I activity ratio (5 out of 27), a little worse for the135I to 131I activity ratio (6 out of 26) and most pro-
nounced for the 133I to 131I activity ratio (14 out
of 43).
The likely explanation for isotopic activity ratios
lying below the theoretical curves are inconsistencies
in the measurements of the different isotopes. The
activity of 131I is often reported as the sum of the
activity on the filter and in the charcoal. However,
due to the measurement method (gross-beta counting
over several days after allowing the short-lived
background to decay) and because of their short
half-lives, the activity of 135I and 133I on the filter is
in most cases below the detection limit at count
time. The activity on the charcoal is measured by
gamma spectroscopy soon after the sampling ended.
Accordingly, only the gaseous part of their activity is
reported, and the atmospheric concentrations of 135I
and 133I are underestimated. As result, their isotopic
Figure 2Model and experimental (x) isotopic activity ratio between 135I and 131I for the 1962 test ‘‘Pampas’’ in a shaft at Nevada Test Site. A is the
delay between the explosion time and the start of the sampling period. B is the duration of the sampling period
Isotopic Characterization of Radioiodine and Radioxenon
Figure 3Comparison of simulated and reported radioiodine isotopic activity ratios between 135I and 133I released from nuclear tests at the Nevada Test
Site. The plot a shows all releases as reported by SCHOENGOLD et al. (1996), the b part applies to all observations made in the wake of the Sedan
test and reported by PLACAK (1963). The simulations use 235U (a) and 239Pu (b) with fission energy neutrons and assumes complete
fractionation at various time steps. The b part (Sedan test) is based on gaseous radioiodine only. For venting and cratering tests, the horizontal
bar indicates the sampling duration, for controlled releases it marks the reported duration of the release (see also Table 1). The X is put at the
time to which the reported activities apply to. These are normally calculated for the mid-point of the collection time but apply to the cloud
passage time, if that was determined
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.
activity ratios with respect to the 131I are shifted
towards too low values.
In order to test this hypothesis and investigate the
isotopic activity ratios without any disturbance by
inconsistent measurements, the plots in Figs. 3b to 5b
display data for the gaseous fraction of radioiodine
only that is trapped on charcoal. All are measure-
ments taken in wake of the Sedan explosion on 6 July
Figure 4Same as in Fig. 3 but for the radioiodine isotopic activity ratios between 135I and 131I
Isotopic Characterization of Radioiodine and Radioxenon
1962 as reported by PLACAK (1963). Only the sample
with the highest concentration is shown in the plot a)
as well. This is the sample taken at Diablo, Nevada,
including the plume cloud passage 3 h after the
explosion. For this sample SCHOENGOLD et al. (1996)
reported a 135I/131I activity ratio for total radioiodine
Figure 5Same as in Fig. 3 but for the radioiodine isotopic activity ratios between 133I and 131I
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.
of 12.5. This is entered in plot of Fig. 4a and lies
below the ensemble of simulated lines. If for both
isotopes only the gaseous fraction is counted as
reported by PLACAK (1963), the activity ratio is 231
and the entry is found within the range of the theo-
retical curves as seen in the plot of Fig. 4b. For the133I/131I the same correction would change the value
from 2.7 (SCHOENGOLD et al., 1996) to 50 according to
PLACAK (1963). This would shift the low entry in
Fig. 5 into the simulated range.
These examples confirm the hypothesis that
inconsistent activity measurements for the different
isotopes could explain why isotopic ratios are found
too low in comparison to the simulated curves. In fact,
the data in the plots of Figs. 3b and 4b are all found
close to or within the range of theoretical lines. In the
plot of Fig. 5b, the majority of data points lie within
the simulation curves, but again two entries are below.
What is more striking however is the fact that the
isotopic ratios are spreading over one order of mag-
nitude even for delay times differing by only 3 h.
Even for samples taken at the same site and at the
same time, the activity ratios differ by a factor of up to
3.3. It is unlikely that any physical or chemical pro-
cess in the cloud causes these differences. Apparently,
the activity measurements are not as reliable as indi-
cated by a two digit reporting precision.
A further strange finding is that the plume has
passed the most distant station (Ely, Nevada) 10 h
after the explosion, but 7 out of 10 data points in
Fig. 5b are determined for times with a delay beyond
10 h and up to 57 h after the explosion. This obser-
vation at Ely is a bit doubtful, because it was a
cratering test that releases most of its activity
instantaneously. Even stranger is a detection of
radioiodine at Lockes, Nevada, determined for about
7 h before the explosion time. These shifted delays
between explosion and detection hint at the possi-
bility that the associations of activity observations to
certain times bear some uncertainties and may in
some instances be off by a few hours for early
detections (before one day has passed) and by a day
for later detections (with delays of several days).
Except for the explained deviations and discussed
outliers, the overall agreement between the mea-
surements at the Nevada Test Site and the model is
reasonable. Most data lie within the ensemble of
simulated curves and their major trends are also
followed by the observational data. These agreements
give confidence in further conclusions drawn from
comparing the reported data and the theoretical cal-
culations. The spread of radioiodine activity ratios of
the observational data centers close to the two lowest
simulation curves, the unfractionated case and the
line that indicates a fractionation time of 1 h after the
explosion. Almost all data are consistent with a
fractionation no earlier than 0.1 h after the explosion.
Accordingly, the radioiodine isotopes and their pre-
cursors remained basically non-fractionated before
the releases took place.
5. Separation of Radioxenon and Radioiodine
in Operational Releases at the Nevada Test
Site
Figure 6 shows the change over time of four
different isotopic activity ratios between radioxenon
and its precursor radioiodine. All ratios are chosen for
the isotopes and isomers that are relevant for nuclear
explosion monitoring and are in the same decay chain
even if no data are available for comparison. The
reported Nevada test release data are shown together
with the theoretical curves for three nuclear explosion
scenarios (the different combinations of fissile iso-
tope and neutron energy spectrum introduced in
section 1) and no fractionation is assumed. Figure 7
shows the same as in Fig. 6 but only for 235U and
fission neutron energy with fractionation of xenon
and radioiodine together from all other precursors at
delays of 0.001, 0.01, 0.1 and 1 h after the explosion.
Again, the effect of fractionation can be seen with the
curve ending its further build-up through the decay
chain and start decaying according to the effective
half-life of the respective radioxenon to radioiodine
activity ratio.
The theoretical curves in Figs. 6 and 7 do not
exhibit a wide spread, in particular not in the time-
frame for data of emissions at the Nevada Test Site
that are available. All data are found below the
simulation curves spreading over many orders of
magnitude. This indicates that radioiodine is in most
cases strongly depleted in the air samples compared
to radioxenon. This depletion does not result from the
Isotopic Characterization of Radioiodine and Radioxenon
Figure 6Change over time of four different isotopic activity ratios between radioxenon and its precursor radioiodine. The simulations with three
nuclear explosion scenarios are compared to reported Nevada test releases. No fractionation is assumed
Figure 7The plots show the same as in Fig. 6 but only for 235U and with fractionation of radioxenon and radioiodine together from the other precursors
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.
common fractionation of iodine and xenon. It is due
to a fractionation between radioxenon and all its
precursors including radioiodine. Partly this may take
place on the way from the explosion cavern to the
surface; partly it can be explained by the filtering of
air prior to its operational release. The data points for
these filtered releases (noted as type 3 in Table 1) are
found to be at least two orders of magnitude lower
than all other entries for the masses 135 and 133 with
the metastable state of radioxenon. For the activity
ratio of 133I and 133Xe, the operational releases with
and without filtering are mixed but most of the fil-
tered releases have a stronger depletion in radioiodine
than most of the unfiltered releases. The strong effi-
ciency of the filtering procedure is obvious with
reduction of the radioiodine content by two to eight
orders of magnitude compared to the theoretical
values.
It remains to be understood why the unfiltered
releases are depleted in radioiodine by one to four
orders of magnitude. The previous section and
Figs. 3, 4, 5 reveal that the radioiodine isotopes and
their precursors remained basically non-fractionated
before the releases took place. This is consistent with
the result of KALINOWSKI (2011) according to which
no significant fractionation between the radioxenon
isotopes and the precursors occurs prior to release on
any of the relevant pathways for operational releases.
The depletion in radioiodine is most likely due to the
passing of the release through a ventilation system
with a filter without this being explicitly reported.
This would imply that the distinction made here
between filtered and unfiltered operational releases is
not strictly applicable. The clear distinction visible in
the figures and described above gives evidence that at
least a difference in the extent of filtering exists.
There are two less plausible explanations for the
depletion in radioiodine which both cannot be veri-
fied from the available data and information. Either
the released radioiodine is not fully accessible to the
measurement or the gas stream that is released by
some kind of operation at the test site is passing
through a natural filtering material prior to the release
and keeping part of the iodine back while fully
releasing xenon.
Since xenon is a noble gas, its release from
an underground explosion depends only on the
availability of an unplugged path from the explosion
cavity to the surface. For iodine, the mobility depends
on its presence in the air stream at the moment a path
opens up. It may be present either in gaseous form or
attached to aerosol particles. Iodine that has con-
densed on or been adsorbed on non-mobile surfaces
will remain underground. On its way out, aerosol
particles may deposit on surfaces and gaseous iodine
may be partially held back by adsorption on surfaces
and by chemical reactions transforming it into a non-
volatile compound. The former is particularly of
relevance, if the air stream happens to be filtered
through a soil column or is purposely pumped
through a particulate filter and activated charcoal
before being released to the atmosphere. According
to CLEMENT et al. (2007) adsorption of iodine has a
significant impact on its volatility and gaseous iodine
can react with radiolysis products of humid air to
form non-volatile oxides or iodate ions.
The conclusion from the investigation of activity
ratios of radioiodine and radioxenon of the same mass
number is that practically for every operational
release radioiodine was to some extent removed from
the gas stream and less radioiodine was released than
the theoretically predicted activity based on the ra-
dioxenon activity.
6. Effect of Fractionation on Source Discrimination
Based on Radioxenon Isotopic Activity Ratios
A robust method for source discrimination has
been demonstrated earlier based on the relationship
of two different isotopic activity ratios (KALINOWSKI
et al., 2010). This requires three or four radioxenon
isotopes to be quantified. In some cases the method
works with the detection limit by substituting a
missing concentration value, if certain isotopes are
not detected. Hence, it is possible to use this method
if only two isotopes are detected. A special advantage
of this new method is its independence on the time
periods elapsed between generation and release as
well as between release and detection, i.e., it is
invariant to dilution and decay.
In Fig. 8, this discrimination method is shown for
the case that all four radioxenon isotopes are mea-
sured and made use of. Two isotopes are used on the
Isotopic Characterization of Radioiodine and Radioxenon
abscissa; the other two are taken for the activity
ratio on the ordinate. The simulation curves entered
here separate the plot area into two distinctive
domains. The trajectories for three operational cycles
of a nuclear reactor follow a circular pattern in
the left half of the plot (KALINOWSKI and PISTNER,
2006). The simulation curves for nuclear explosion
scenarios remain in the right half of the plane. In
order to illustrate the power of this source discrimi-
nation method, the observational data of the
International Noble Gas Experiment (INGE) are
shown in the same plot as used in the similar plot by
KALINOWSKI et al. (2010). This demonstrates that the
method is robust against the typical measurement
errors and a separation line can be defined that leaves
most observations of ambient air in the reactor
domain.
The change in the isotopic ratios is shown for
complete fractionation involving only the indepen-
dent yields (pure radioxenon curve) and without any
fractionation allowing for in-growth (unfractionated
decay chain curve). Depending on the amount of
fractionation of the radioxenon isotopes from their
parents, the actual ratios will fall between the two or
precisely on one of the lines.
Figure 9 shows the same as Fig. 8 but with the
assumption that radioxenon and radioiodine are
together separated from the precursors.
In each plot, a separation line is drawn between
the reactor and the explosion domain. Any isotopic
activity ratio combination on the separation line
moves down along that line with the radioactive
decay. Any isotopic activity ratio combination off
that line remains on the same side of the line forever.
Radioactive decay changes the isotopic activity ratios
along a line that is parallel to the separation line.
In Fig. 9, the left lines bounding possible isotopic
activity ratios of the three nuclear explosion scenarios
remain the same as in Fig. 8. These are valid for the
case without any fractionation. Accounting for radi-
oiodine separating from the non-volatile precursors
together with radioxenon affects all other lines, in
Figure 8Time-invariant source discrimination based on radioxenon isotopic activity ratio relationship with reactor emission data for the case that all
four isotopes are measured (KALINOWSKI et al., 2010). The dashed line marks the time-invariant screening separation. All isotope ratio relations
found above (i.e., left to) this line can be screened out, i.e., the related samples are definitely irrelevant for CTBT verification purposes,
because they cannot be explained by a nuclear explosion. All samples that have ratio dependencies found below (i.e., right to) the line might
be relevant for CTBT monitoring purposes. The exact location of the separation line is subject to further studies. The expected isotopic ratios
present at t = 0 are denoted with the ‘‘closed circle’’ symbol, and different lines styles are used to show the change in the isotopic ratios for
the different fractionation scenarios. Time steps of the first four full days are marked on these lines with ‘‘?’’ symbols. For 235U, the daily time
steps for 1–10 days of delay after the explosion are marked with thin solid lines to indicate were other fractionation scenarios would be at the
daily time steps
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.
particular the position of the right boundary lines.
They are bent towards the separation line in Fig. 8.
The conclusion of this comparison is that no kind of
fractionation compromises the clear separation of the
nuclear explosive domain from emissions of nuclear
reactors.
7. Conclusions and Implications for Monitoring
for Nuclear Explosions
This paper studies the temporal development of
radioxenon and radioiodine activities with two dif-
ferent assumptions on fractionation. In the first case
only the noble gases are released, in the second case
radioiodine is released as well while the precursors
remain underground. For the second case, the simu-
lated curves of activity ratios are compared to prompt
and delayed atmospheric radioactivity releases from
underground nuclear tests at Nevada as a function of
the time of atmospheric air sampling for concentra-
tion measurements of 135I, 133I and 131I. Most of the
data from the Nevada Test Site lie at the lower end of
the simulated curves indicating either no fraction-
ation of radioiodine from its precursors at all or a
fractionation not earlier than 0.1 h and more likely
later than 1 h after the explosion. Accordingly, the
radioiodine isotopes and their precursors remained
basically non-fractionated before the releases took
place.
The conclusion from the investigation of activity
ratios of radioiodine and radioxenon of the same mass
number is that practically for every operational
release iodine was to some extend removed from the
gas stream and less radioiodine was released than the
theoretically predicted activity based on the radiox-
enon activity.
The final conclusion is that no kind of fraction-
ation can compromise the clear separation of the
nuclear explosive domain from emissions of nuclear
reactors that can be used for source discrimination
based on the relationship of two different radioxenon
isotope activity ratios.
Acknowledgments
This work was funded by the German Foundation for
Peace Research (DSF) and the University of Ham-
burg. The authors are grateful to the two reviewers
for their questions and suggestions that helped to
improve on the manuscript.
Figure 9This plot shows the same as in Fig. 8 but with the assumption that radioxenon and radioiodine are together separated from the precursors
Isotopic Characterization of Radioiodine and Radioxenon
REFERENCES
BATEMAN, H. (1910), The solution of a system of differential
equations in the theory of radio-active transformation. Proc.
Cambridge Phil. Soc., 16, 423.
CLEMENT, B., CANTREL, L., DUCROS, G., FUNKE, F., HERRANZ, L.,
RYDL, A., WEBER, G., WREN, C. (2007), State of the art report on
iodine chemistry, Nuclear Energy Agency, Committee on the
Safety of Nuclear Installations. Report NEA/CSNI/R(2007)1,
February 2007.
DE GEER, L.-E. (2001), Comprehensive Nuclear-Test-Ban Treaty:
Relevant radionuclides. Kerntechnik 66(3), 113–120.
ENGLAND, T.R., and RIDER, B.F. (1994), Evaluation and Compila-
tion of Fission Product Yields: 1993. Los Alamos report LA-UR-
94-3106 (ENDF-349), Appendix A (Set A Yields Evaluated and
Compiled), October 1994.
HOFFMANN, W., KEBEASY, R., and FIRBAS, P. (1999), Introduction to
the verification regime of the Comprehensive Nuclear-Test-Ban
Treaty. Phys. Earth Planet. Interiors, 113, 5–9.
KALINOWSKI, M.B. (2006), Comprehensive nuclear-test-ban treaty
CTBT verification. In: R. AVENHAUS, N. KYRIAKOPOULOS, M.
RICHARD, G. STEIN (Eds.), Verifying Treaty Compliance. Springer
Berlin, Heidelberg 2006, pp. 135–152.
KALINOWSKI, M.B. (2011), Characterisation of prompt and delayed
atmospheric radioactivity releases from underground nuclear
tests at Nevada as a function of release time. J. Environ. Ra-
dioact. 102(9), 824–836. doi:10.1016/j.jenvrad.2011.05.006.
KALINOWSKI, M.B., LIAO, Y.-Y., and PISTNER, C. (2012), Discrimi-
nation of nuclear explosions against civilian sources based on
atmospheric radioiodine isotopic activity ratios. Submitted to
Pageoph Topical Volume II on Recent Advances in Nuclear
Explosion Monitoring.
KALINOWSKI, M.B., and PISTNER, Ch. (2006), Isotopic signature of
atmospheric xenon released from light water reactors, J. Envi-
ron. Radioact. 88(3), 215–235.
KALINOWSKI, M.B., and SCHULZE, J. (2002), Radionuclide monitor-
ing for the comprehensive nuclear-test-ban treaty. J. Nuclear
Mater. Manag. 30(4), Summer 2002, 57–67.
KALINOWSKI, M.B., AXELSSON, A., BEAN, M., BLANCHARD, X.,
BOEYER, T.W., BRACHET, G., HEBEL, S., MCINTYRE, J.I., PETERS, J.,
PISTNER, C., RAITH, M., RINGBOM, A., SAEY, P., SCHLOSSER, C.,
STOCKI, T.J., TAFFARY, T., and UNGAR, R.K. (2010), Discrimina-
tion of nuclear explosions against civilian sources based on
atmospheric xenon isotopic activity ratios. In: B ECKER, A.,
SCHURR, B., KALINOWSKI, M.B., KOCH, K., BROWN, D. (Eds.),
Recent Advances in Nuclear Explosion Monitoring. Pure and
Applied Geophysics Topical, vol. 167/4-5, S.517–539. doi:
10.1007/s00024-009-0032-1.
LIAO, Y.-Y. (2011), Fraktionierung bei der Freisetzung von Leit-
nukliden fur die Entdeckung von unterirdischen Kernwaffentests.
Diplomarbeit, Universitat Hamburg, September 2011.
PLACAK, O.R. (1963), Project Sedan, Final Off-Site Report, U.S.
Public Health Service, Report PNE-200F, 25 April 1963.
SCHOENGOLD, C.R., DEMARRE, M.E., and KIRKWOOD, E.M. (1996),
Radiological effluents released from U.S. continental tests 1961
through 1992, United States Department of Energy - Nevada
Operations Office. DOE/NV-317 (Rev.1) UC-702, Las Vegas,
August 1996.
USPHS (1964), Final Report of Off-Site Surveillance for OPER-
ATION NOUGAT September 15, 1961–June 30, 1962. U. S.
Public Health Service, Department of Health Education and
Welfare, Off-Site Radiological Safety Program, Southwestern
Radiological Health Laboratory, Las Vegas, Nevada, April 24,
1964. (SWRHL-1r).
(Received March 13, 2012, revised August 2, 2012, accepted August 12, 2012)
M. B. Kalinowski, Y.-Y. Liao Pure Appl. Geophys.