Design and Performance of the Integrated Waste Assay System (IWAS)
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Presented at the 44th Annual meeting of the INMM, July 13-17, 2003, Phoenix, AZ |
Robert D. McElroy, Jr., Stephen Croft, Brian Young, Ludovic Bourva
CANBERRA Industries, Inc., Meriden, CT USA||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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| Figure 1. Sketch of the layout of the IWAS assay cavity. The figure at left shows the AAS source interrogation position in the center of the rotator assembly. The figure at right shows the location of the four fast Cd covered neutron detection packages (FNDP). |
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| Figure 2. Measured performance of the Add-A-Source correction technique for uniform source and matrix distributions. The solid bars show the relative performance prior to application of the AAS correction. |
The AAS measurement is also used in the active neutron analysis and in correction of the passive neutron background levels. Additional discussion is presented in the following sections.
Passive Neutron Detection Levels
The passive neutron detection levels for the IWAS system are similar to those provided by the HENC. The detection levels are highly sensitive to the location of the assay facility (note that the cosmic-ray flux increases with altitude) and the construction of the assay building itself (heavy concrete structures reduce the cosmic-ray flux reaching the assay system. Table 2 provides the approximate detection levels for the IWAS systems for weapons grade plutonium with 10 minutes passive acquisition time in a non-interfering matrix. Passive neutron multiplicity counting allows cosmic-ray fluctuations to be suppressed.
Table 1.
Comparison of HENC and IWAS passive neutron performance.
| Passive Assay Parameters | IWAS | HENC |
| 3He Proportional Tubes | 122 | 113 |
| 3He partial pressure | 7.5 atm | 7.5 atm |
| Efficiency, 240Pu, Spontaneous Fission Neutrons | 27% | 31% |
| Die-Away Time | 45 µs | 50 µs |
| Characteristic Dead time | 29.6 ns | 111 ns |
| Doubles Gate Utilization Fraction | 0.71 | 0.59 |
| Pre-delay | 4.5 µs | 4.5 µs |
| Gate Width | 128 µs | 128 µs |
| Sensitivity (Reals Rate in cps/g 240Pueff) | 46.8 | 52 |
Table 2.
Measured Passive Neutron Coincidence counting detection levels for the IWAS.
| Altitude | Building Type | Coincidence Background | Detection Level (240Pueff) |
| 30 meters | Light structure | 1.1 Reals/second | 4.6 mg |
| 1600 meters | Light structure | 3.7 Reals/second | 8.3 mg |
| 1600 meters | Heavy concrete structure | 0.24 Reals/second | 2.2 mg |
induce fission in the plutonium and uranium contained within the drum. Neutrons from the induced fission events are detected in a sub-set of the 3He tubes that are mounted in cadmium wrapped HDPE packages. The difference in the characteristic decay time for the source neutrons to thermalize and induce fission and the characteristic decay time for neutrons to be detected gives the technique its sensitivity.
The design of the IWAS system is a balance between the active neutron sensitivity and the passive neutron detection efficiency. The large number of high pressure 3He tubes required for the passive neutron counting tends to poison the interrogating neutron flux from the generator. Optimizing the counter for active interrogation tends to decrease the passive counting efficiency and increase the characteristic die-away time for the counter.
The active neutron detection system consists of four separate Fast Neutron Detector Packages (FNDP) arranged as in Figure 1 above. The FNDP contain either three or four 3He tubes each embedded in cadmium wrapped HDPE moderator blocks. To minimize dead-time losses, each of the 12 3He tube has its own 111A pre-amp/amplifier discriminator board. A single FNDP is located in each of the vertical walls of the assay cavity as shown in Figure 1. In addition to the FNDP detection assemblies, the active measurement requires two flux monitors. These are low pressure 3He tubes of 15 cm active length used to monitor the neutron output of the generator (cavity flux monitor) and to estimate the neutron flux within the drum (barrel flux monitor). Data is acquired using four multichannel scalers modules recording the FNDP, flux monitor and total neutron count rates as a function of time following the Zetatron pulse. A typical assay is comprised of 12,000 pulses from the generator operating with a repetition rate of 100 Hz. The measured performance parameters for the active mode are given in Table 3.
The active mode detection levels were examined by performing multiple assays on several type of matrix drum. The resulting detection levels are given in Table 4. These are based on 5% Type I and Type II errors.
Table 3.
Active Neutron Interrogation Performance Values.
| Induced Fission Neutron Efficiency | 2.8% |
| Fission Neutron Effective Die-Away Time | 28 µs |
| Zetatron Pulse FNDP Detection Efficiency | 0.7% |
| Zetatron Pulse FNDP Die-Away Time | 38.2 µs |
| Early Gate Start | 625 µs |
| Early Gate Width | 1374 µs |
| Sensitivity (counts/g 239Pu/108 neutrons) | 38 |
| Background Rate (includes ambient) | 0.08 counts/pulse in early gate |
| MDA (239Pu) empty drum | 9 mg |
Table 4.
Measured Limits of Detection for representative matrix types.
| Matrix Description | Detection Level |
| Empty Drum | 12 mg 239Pu |
| 50 kg combustibles | 8 mg 239Pu |
| 65 kg HDPE beads/vermiculite | 11 mg 239Pu |
| 150 kg surrogate sludge (PDP standard) | 30 mg 239Pu |
| 220 kg scrap steel | 21 mg 239Pu |
Gamma-Ray Sub-System
The gamma-ray analysis sub system is based on the CANBERRA Q2 system approach8. The Q2 system uses multiple HPGE detectors mounted in a 4p low background steel shield and a close coupling between the HPGE detectors and waste container to provide very low detection levels. The IWAS design target was 30 nCi/gram of TRU activity in 700 seconds count time. The system also needed to provide plutonium and uranium isotopic measurements. To achieve this goal, two CANBERRA BE2820 Broad Energy Germanium (BEGe) detectors were selected (refer to Figure 3). The 40 cm plus thickness of HDPE provides an effective gamma-ray shield to minimize background effects and the inadvertent movement of a drum past the system.
The IWAS systems are fully automated and intended to perform many thousand assays per year. Exposure to the active neutron interrogating flux would render the detectors useless after only a few assays if not protected. To extend the life of the detectors, the detectors are automatically retracted from the assay cavity and shielded by thick plugs made from HDPE and cadmium. With this provision, the detector life time is estimated to be from 15,000 to 20,000 thousand active assays.
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| Figure 3. Photograph of the IWAS system. The retractable HPGe detector assemblies are seen at the left of the counter. |
Waste drums containing several Ci of 241Am are expected so the detectors were purposefully shielded to eliminate almost all of the 60 keV gamma-rays. A 0.1 cm of cadmium layer was added to the front face of the BEGe detectors in addition to the 0.8 cm of stainless steel required for the assay cavity liner. Test measurements indicate source loadings of 10 Ci 241Am will result in dead times of less than 30%. Note that the quantification measurements for this arrangement do not use the characteristic 60 keV line from 241Am. Instead a weighted average based on the 125, 662 and 722 keV lines provides an assay result less dependent on the matrix effects than if the 60 keV line were used. Interference corrections are applied if significant quantities of 137Cs are present.
Gamma-Ray Detection Levels
The detection limits for the gamma-ray system are given in Table 5. Detection limits are based on the measured efficiency profiles for the system and measured spectra for surrogate waste matrices. The 239Pu detection level for the 0.1 g/cc waste drum is approximately 10 mg for a source located at the point of least sensitivity.
ANALYSIS ENHANCEMENTS
The IWAS system analysis software includes several enhancements to the traditional analysis techniques. The more important enhancements are listed in the following paragraphs.
Passive Neutron Coincidence Background Corrections
The coincidence neutron background has two primary sources, the presence of nearby fission sources and cosmic-ray induced neutron events. The IWAS shielding is sufficient to remove most of the ambient neutron background but can not eliminate the neutrons generated by cosmic-rays interacting with the counter’s body or the contents of the sample. Drums containing lead or steel have an associated cosmic-ray induced
Table 5.
IWAS Gamma System Detection Levels (uniform matrix, 660 second count times).
| Nuclide | Energy (keV) |
Typical LLD (pCi/g)a Density (g/cc) |
Worst Case LLD (pCi/g)b Density (g/cc) |
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| 0.1 | 0.3 | 0.8 | 1.8 | 0.1 | 0.3 | 0.8 | 1.8 | ||
| 137Cs 60Co 232Th 238U 235U |
662 1173 908 1001 185 |
0.72 0.65 2.2 93 1.6 |
0.32 0.26 1.0 39 0.75 |
0.20 0.17 0.6 24 0.55 |
0.16 0.13 0.5 20 0.5 |
1.04 0.86 2.9 126 2.3 |
0.52 0.39 1.6 60 1.4 |
0.60 0.39 1.5 61 3.2 |
1.76 0.69 3.2 135 21.5 |
| Pu detection levels in nCi/g | |||||||||
| 239Pu | 414 | 19.9 | 9.0 | 8.5 | 5.6 | 30 | 16 | 25 | 124 |
a. Detection levels for a nominal 600 second passive assay.
b. Estimated detection levels for a non-self attenuating point source at the position of lowest sensitivity in the drum.
coincidence background (or interference) that results in a positive bias in the reported mass if not corrected. Conversely, highly moderating drums (e.g., sludges) tend to attenuate the cosmic-ray induced coincident neutrons potentially resulting in a negative bias. The IWAS can correct for these effects using the AAS correction measurement and multiplicity analysis9.
The moderator content of the drum affects the coincident neutron background rate in a similar manner as it affects the fission neutron emission rate. Coincidence rates were measured for a series of surrogate matrix drums including metals, sand, soils, plastics and combustibles. Figure 4 shows the ratio of the measured coincidence rate for these drums relative to an empty drum measurement as a function of the measured AAS correction factor. Failure to correct for this effect results in a negative bias in the reported plutonium mass. The magnitude of this effect depends on the system and overall neutron background rates, but for typical sludge matrix drum (Add-a- Source correction factor equal to five) the bias can be as large as 2 g weapons grade plutonium. The IWAS system incorporates a patented correction algorithm to eliminate this bias9.
High-Z materials such as steel and lead, create a background of coincident neutrons due to the interaction of cosmic-rays and with the waste matrix. At high enough elevations, such as at Los Alamos or Rocky Flats, a 100 kg of steel can result in a 0.5 gram positive bias in the reported plutonium mass. Methods such as
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| Figure 4. AAS based background correction factor eliminates the negative bias that occurs for highly moderating waste matrices. |
statistical filtering and truncation of the multiplicity histogram have been employed to minimize the effect of these high-Z materials but these methods do not completely eliminate the bias. A correction for the high-Z content of the waste item has been developed based on multiplicity analysis. In a manner similar to the separation between plutonium and curium10, the analysis takes advantage of the difference in the moments of the multiplicity distribution between plutonium and cosmic-ray induced events. The analysis effectively measures the high-Z content of the waste matrix and corrects the reported plutonium mass.
Active Neutron Detection – Moderator Index
The IWAS active neutron interrogation method follows the basic approach of the second generation Differential Die-Away method8 but the treatment of the matrix correction factors has been extended to more accurately correct for uranium and low Pu mass samples. The traditional approach has been to use the passive neutron count rates to calculate a moderator index and moderator correction factor. Samples containing uranium only or small levels of plutonium do not provide a useful passive neutron count rate. Also biases can occur due to the shift in average neutron energy for samples with high (a, n) emission rates. However, this system calculates the moderator index from the measured Add-A-Source correction factor allowing the calculation of the moderator correction for these problem sample types. Figure 5 shows the effectiveness of the matrix corrections for a High Enriched Uranium (HEU) sample.
Total Measurement Uncertainty
While it is still quite common for the Total Measurement Uncertainty (TMU) to be calculated in a post assay analysis, or simply assigned on a waste stream basis, the IWAS approach calculates the TMU for each of the analysis modes for each drum. The TMU calculation is based on measured parameters, such as matrix correction values, drum weight, count times, etc. and the result is then used in determination of the suitability of the assay result for disposition of the drum. All of the information required for processing is handled by the NDA 2000 software.
INTEGRATED APPROACH
The physical integration approach of the IWAS system was driven primarily by a desire to limit floor space requirements and improve throughput. Without the need to load/unload/transport the drum between instruments, material handling is minimized and there is greater time available for assay. Because all measurements are made in a single chamber there is little likelihood that the gamma-ray results from one drum will be integrated with the neutron results of another, so data quality is improved.
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| Figure 5. Relative performance of the active neutron matrix correction using the AAS based moderator index for an HEU point source. The results displayed relative to the effective uranium mass (0.28 grams 235U). |
The IWAS integrates not only the multiple assay techniques into a single measurement chamber it also provides a fully integrated data analysis. The process is not based an Artificial Intelligence approach, but instead the software attempts to emulate the data review steps that would be followed by an NDA specialist. The analysis software integrates the results from the passive neutron, active neutron and gamma-ray analysis measurements and AK using a well defined set of logic steps to choose the “best” assay result. The observed count rates, dead times, matrix correction factors, plutonium isotopic abundances, etc., are compared against a set of action levels to determine first the acceptability of each analysis method, and then to select the best result from the valid methods based on a well defined hierarchy. For example, should the drum weight of the drum exceed the alarm point, the quantitative gammaray result is considered invalid and the assay report is flagged for review by an NDA expert. Should multiple techniques, say quantitative gamma analysis and active neutron both return acceptable results, the technique that results in the lowest TMU is selected (there is no attempt to average the results from two or more techniques). Additionally, if two or more results are considered valid, the results are compared and if they do not agree within the TMU values, the results are considered suspect. The layered consistency checks help to ensure that problem drums are identified prior to review by the NDA personnel and minimizing the chances for mischaracterization.
SUMMARY
The IWAS system provides NDA results using the three most commonly used analysis techniques integrated both physically and analytically. New analytical techniques have been developed to improve the quality of data available from each of the assay techniques and to lower the sensitivity and TMU available as individual measurements. The automated combination of results provides improved accuracy and reliability of the final assay values. Four systems are in or are about to enter service. The first two have successfully passed round nine of the PDP trials.
REFERENCES
- “Contact-Handled Transuranic Waste Acceptance Criteria for the Waste Isolation Pilot Plant”, DOE/ WIPP-02-3122, July 25, 2002.
- “Waste Description Information for Transuranic- Contaminated Wastes Stored at the Idaho National Engineering Laboratory” INEL-95/0412 Appendix A and Appendix B, December 1995.
- H. Menlove, et. al. “HENC Performance Evaluation and Plutonium Calibration”, LA-13362-MS, October, 1997.
- Judith F. Briesmesiter, LA-12625-M, Version 4B, “MCNPTM – A General Monte Carlo N-Particle Transport Code Version 4B”, March 1997.
- H. Menlove, et. al., “WDAS Operation Manual, Including the Add-A-Source Function”, LA-12292- M, April, 1992.
- H. Menlove, et. al., “NBC Operation Manual, Including the Multi-position Add-A-Source Function”. LA-12737-M.
- J. T. Caldwell, “Calibration, Matrix Corrections, and Verification Activities with the Los Alamos Second Generation Combined Passive and Active Neutron Assay Systems”, Document Q2- TN-85-102, May 1985.
- F. Bronson, “Q2 – A Very Low Level Quantitative and Qualitative Waste Assay and Release Certification”, Proceedings of Waste Management ’90, Tucson, Arizona, February, 1990.
- R.D. McElroy, et. al., “Method for reduction in the interference of cosmic ray-induced neutron events in passive neutron coincidence and multiplicity counting”, US Patent #6,509,563.
- P. Rinard et. al. “Applications of Curium Measurements for safeguarding at Large-scale Reprocessing Plants”, ESARDA 19th Annual Symposium on Safeguards and Nuclear Material Management Proceedings (ESARDA 28; EUR 17665 EN), 1997 PP. 221-5.
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