pulses in the range of counting rates differing by more than six orders of magnitude.
Passive systems of neutron coincidence counting allow determining the mass of plutonium by logging spontaneous-fission neutrons of mostly evennumbered isotopes (238Pu, 240Pu, 242Pu). With plutonium isotope composition known, the measurement result – 240Pueff mass – can be converted to the total Pu mass in the sample.
The fissionable isotope 235U does not go into spontaneous fission readily enough to be logged by passive systems. In this case, instruments will register secondary induced neutron radiation, which arises under exposure to neutrons of an AmLi source (active systems). For low-energy incident neutrons, the induced fission of 238U in a specimen makes an insignificant contribution to the measured rate of neutron coincidences.
Neutron coincidence counting systems have detectors of two major configurations: well-type detectors in which a specimen is fully enclosed and collar-type detectors embracing a specimen from the outside. The geometry of the former detectors is preferable as it is possible in this case to register all emitted neutrons. But the alternative collar-type geometry allows measuring specimens too large to be placed in a well-type detector (e.g., a fuel assembly). In its inspection activities, the IAEA employs neutron instruments of more than 20 types, which have various design features and are usable for specimens of certain sizes and forms and various Pu and U mass ranges. Some of them are presented in Table 3.5.
Table 3.5
Neutron coincidence logging instruments in use for determining the mass of fissionable material
Instrument |
Instrument name |
Application and features |
designation |
and type |
|
|
Passive neutron coincidence counters |
|
FAAS |
Fuel |
Meant for checking Pu mass in non-irradiated |
|
assembly/Capsul |
MOX fuel assemblies. |
|
e Assay System |
|
HLNC |
High-Level |
Meant for checking Pu mass (from 20 g to 2 kg) |
|
Neutron |
in bulk materials (pellets, powder, scrap, etc.). |
|
Coincidence |
|
|
Counter |
|
INVS |
Inventory |
Meant for checking Pu mass (from 0.1 g to 300 |
|
Sample Counter |
g) in samples. Instrument options for checking |
|
|
Pu mass in glove boxes. |
76
|
|
|
|
Table 3.5 (continued) |
|
|
|
|
|
||
Instrument |
Instrument name |
Application and features |
|
||
designation |
and type |
|
|
|
|
|
|
Active neutron coincidence counters |
|
||
AWCC |
Active Well |
Meant for checking 235U content in samples with |
|
||
|
Coincidence |
highly enriched uranium. |
|
||
|
Counter |
|
|
|
|
UNCL |
Uranium |
Meant for checking |
235U content in low- |
|
|
|
Neutron |
|
enrichment fuel assemblies. |
|
|
|
Coincidence |
|
|
|
|
|
Collar |
|
|
|
|
WCAS |
Waste |
Crate |
Meant for checking |
waste for presence of |
|
|
Assay System |
nuclear material. |
|
|
|
Non-destructive testing of irradiated nuclear material. Methods of checking irradiated nuclear fuel involve logging of neutrons and gamma– quanta, as well as the Cerenkov ultraviolet glow. Fission products found in irradiated fuel set up a very high radiation background. It is mainly this fact that determines the type of instruments employed for verification of spent fuel.
The main sources of neutrons emitted by spent fuel are spontaneously fissionable 242Cm and 244Cm. These isotopes are generated in a reactor when neutrons are successively captured by the nuclei of transuranic elements. There are several approaches to logging spent fuel neutrons under conditions of intensive gamma background. It is possible, for example, to choose such detectors that either will be insensitive to gamma radiation, or will protect a neutron detector from penetration of gamma rays, while letting in neutrons. Table 3.6 lists some measurement systems in use by the Agency for examining reactors’ spent fuel.
77
|
|
Table 3.6 |
|
|
Spent fuel testing instruments |
||
|
|
|
|
Instrument |
Instrument |
Application and features |
|
designation |
name and |
|
|
|
type |
|
|
|
|
|
|
FDET |
Fork Detector |
The detector head contains neutron detectors |
|
|
Irradiated |
insensitive to gamma radiation (four gas-filled |
|
|
Fuel |
proportional fission counters) and two gas-filled |
|
|
Measuring |
ionization chambers to match strong gamma |
|
|
System |
radiation. The ratio between neutron and gamma |
|
|
|
data together with additional information of |
|
|
|
another sort allows getting an idea of the fluence |
|
|
|
received, of the initial content of fissionable |
|
|
|
material, and of the number of in-pile irradiation |
|
|
|
cycles. |
|
SFAT |
Spent Fuel |
The instrument includes a multichannel gamma– |
|
|
Attribute |
radiation analyzer and a NaIor CdZnTe-based |
|
|
Tester |
detector. It can accurately detect irradiated fuel by |
|
|
|
identifying the characteristic lines from 137Cs and |
|
|
|
144Pr fission products and 60Co as an activation |
|
|
|
product. The instrument is particularly helpful in |
|
|
|
situations where the Cerenkov effect analyzers are |
|
|
|
not easily useable. |
|
ICVD, |
Cerenkov |
ICVD is a hand-held instrument employed for |
|
DCVD |
Viewing |
identification of irradiated fuel assemblies from, |
|
|
Device, |
mostly, light water reactors by analyzing the |
|
|
Digital |
Cerenkov effect. DCVD is a highly sensitive |
|
|
Cerenkov |
digital device for analyzing the Cerenkov effect. It |
|
|
Viewing |
is particularly suitable for fuel of low burnup after |
|
|
Device |
prolonged cooling. |
|
Destructive analysis techniques. Destructive measurements practiced to determine the element and isotope composition are applicable to all forms of bulk material found at nuclear fuel cycle facilities. Such measurements enable the Agency:
∙ to make sure that there were no long-term diversions of materials covered by the safeguards;
78
∙to verify the quality of working standards in use for calibration of nondestructive analysis instruments;
∙to carry out periodic verification of measurement systems at the inspected facility.
In general, destructive verification measurements carried out by the Agency include the following successive stages:
1)independent sampling;
2)in-situ conditioning of samples to ensure their integrity during transportation;
3)packaging, sealing and dispatch of samples to the IAEA laboratories;
4)statistical estimation of the analysis results.
The main analytical methods of destructive testing practiced by the Agency during inspections are listed in Table 3.7. This table presents the estimated random and systematic components of errors in measurements of materials of nuclear grade or similar chemical purity. It is obvious that the sampling process itself or the presence of impurities in material can tangibly affect the data of Table 3.7.
|
|
|
|
|
Table 3.7 |
|
|
Main destructive analysis methods in use by the IAEA |
|
|
|||
|
|
|
|
|
|
|
|
Method |
Measured |
Type of |
Error, |
|
|
|
|
quantity |
material |
( % rel.), random |
|
|
|
|
|
analyzed |
and systematic |
|
|
|
|
Element analysis |
|
|
|
|
Potentiometric titration |
|
U, U–Pu, U–Th a) |
|
|
|
|
of U (Davis–Gray |
U |
0.05 |
0.05 |
|
||
method) |
|
|
|
|
|
|
Potentiometric titration |
|
Pu materialsa) |
|
|
|
|
of Pu (McDonald- |
Pu |
0.1 |
0.1 |
|
||
Savage method) |
|
|
|
|
|
|
Calorimetry of Pu |
Pu |
Pure Pu materials |
0.1 |
0.1 |
|
|
solutions |
|
|
|
|
|
|
Gravimetry with baking |
U |
Pure U oxides |
0.05 |
0.05 |
|
|
X–K |
fluorometric |
Pu |
Pu materialsa) |
0.2 |
0.2 |
|
analysis |
|
|
|
|
|
|
X-ray fluorescence |
|
Pure U and Pu |
|
|
|
|
spectrometry |
Pu, U |
oxides and MOXa) |
0.3 |
0.3 |
|
|
Mass– spectrometry with |
U, Pu |
Starting solutions of |
|
|
|
|
isotopic dilution |
|
spent fuel, Pu and |
0.1 |
0.1 |
|
|
|
|
|
U–Pu materials |
|
|
|
79
|
|
Table 3.7 (continued) |
|||
|
|
|
|
|
|
Method |
Measured |
Type of |
Error, |
|
|
|
quantity |
material |
( % rel.), random |
|
|
|
|
analyzed |
and systematic |
|
|
|
Isotope analysis |
|
|
|
|
Thermal-ionization |
|
All Pu and U |
0.05 b) |
0.05 b) |
|
mass–spectrometry |
U, Pu |
materials, starting |
|
||
|
isotopes |
solutions of spent |
|
|
|
|
|
fuel |
|
|
|
Gamma–spectrometry of |
Pu |
Pure U and Pu |
0.5–2.0 |
0.5–2.0 |
|
high resolution (Ge- |
isotopes, |
materials |
|
|
|
based detector) |
Am, Np |
|
|
|
|
Gamma–spectrometry |
235U |
LEU materials |
|
|
|
(NaI-based detector) |
|
0.2–0.5 |
0.2–0.5 |
|
|
Alpha–spectrometry |
238Pu |
Pu materials |
0.2 |
0.3 |
|
a)excepting INF;
b)for ratios of the main isotopes.
Safeguards-related activities of the IAEA
The inspection activities of the IAEA depend on the scale of nuclear operations carried out by a state. These operations will be small-scale in states having, e.g., one small research reactor alone, but can be quite extensive in countries with many nuclear fuel cycle facilities. The scope of inspection activities is the greater, the larger is the number of NFC facilities in a country. Table 3.8 presents rough estimates of the nuclear material quantities covered by the IAEA safeguards. It may be seen that the NM quantities under control are steadily growing, and so is the number of facilities under the IAEA safeguards.
This being so, the inspection activities, including independent measurements of nuclear materials and their control by means of containment and surveillance techniques, depend largely on the type of nuclear facilities under the safeguards. Reactors and storage facilities, where materials appear as articles, such as fuel assemblies, call for less inspection effort than do facilities with materials found in bulk, where the greater part of NM is in motion or under processing. Table 3.9 shows the numbers of various facilities covered by the IAEA Safeguards.
80