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ISOTOPIC gamma spectroscopy waste determination

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ISOTOPIC gamma spectroscopy waste determination

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Brief description:ISOTOPIC provides practical solutions to various gamma ray radiation measurement problems encountered in site characterization and waste container measurement

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ORTEC ISOTOPIC Advanced Solution to Gamma Ray Waste Assay
ISOTOPIC provides practical solutions to various gamma ray radiation measurement problems encountered in site characterization and waste container measurement. The easy-to-use software builds on initial work by several U.S. Department of Energy (DOE) laboratories analyzing thousands of fissile waste containers and references methods developed by the Energy Measurement Laboratory (EML-NYC) for measuring contamination over large areas of soil and land surfaces. ISOTOPIC can run under the latest 64-bit operating system and supports most ORTEC spectroscopy hardware products. It is worth mentioning that ISOTOPIC is the software part of the ISO-CART-85 mobile low-level radioactive waste analysis system. ISOTOPIC ensures practicality, flexibility and accuracy of results through the use of traceable calibrations.
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    ISOTOPIC provides practical, integrated solutions for a variety of gamma ray measurement problems encountered in radioactive waste analysis and characterization applications. It analyzes high-resolution, high-purity germanium (HPGe) spectra and determines results for large sample volumes.

    ISOTOPIC can be used "out of the box" as part of an easy-to-operate mobile system (such as the ORTEC ISO-CART-85) or integrated into automated systems, for example, for high-throughput measurements of large vessels in decommissioning projects.

    Applicability
    Applicable to the following geometries:

    • Box, barrel, tube or surface (collimated detector)
    • Closed geometric small containers (e.g. bottles with end caps)
    • Large area determination of soil and surface (non-collimated detector: M-1 method)

    ISOTOPIC offers a number of standard geometry "templates" from which specific measurement configurations can be developed. These templates include cylinders (from top and sides; including lined cylinders (pipes)), boxes, point sources (far field), closed geometric small containers with end caps, and infinite planes. The bottle counting option on the ISO-CART-85 is an example of a "with end cap" closed geometry. The Infinite Plane (Soil) mode provides non-collimated measurements of contamination, shedding or large-area leaks washed into or on an Infinite Plane, i.e. measurements of soil above the ground.

    method
    In container mode, for counting packages, pipes and surfaces, the detector is calibrated with a single point source measurement, even when using a collimator. This primary calibration meets any detector's certification standards and can be extrapolated or modeled to match the sample's physical conditions, container geometry, materials, and matrix composition. The model is based on a "point-kernel" approach, which decomposes the entire measurement problem into multiple source/matrix pixels and calculates and sums their contributions to the composite spectrum. This method is similar to the Monte Carlo method, utilizing user-supplied detector parameters (crystal diameter, crystal length, dead layer and end cap thickness) as part of the measurement configuration. No special individual measurements are required to calibrate the detector other than a single point source calibration.

    ISOTOPIC includes an improved "closed geometry" algorithm where the distance between detector and container is less than 15 cm.

    For non-collimated large area soil counting, the "1 meter" method developed by the US DOE EML2 and later extension 3 can be used. It works in many situations:

    • Conduct decontamination assessments of previously used sites
    • Assessment of nuclides deposited during emergencies
    • Routine environmental monitoring near nuclear facilities

    The EML method simplifies complex measurement problems into the product of three easily determinable factors. The gamma ray peak area is related to a specific nuclide activity by the product of three factors. Factors for a range of detector types and soil conditions have been identified and listed within the program. Efficiency calibration is determined using the efficiency specified by ANSI/IEEE 325-1996 at 1.33 MeV and the crystal length and diameter.

    To improve accuracy at low energies, the user can use the same calibration as in vessel mode instead of the EML method.

    No special (and expensive) Monte Carlo calibration of the detector is required. Determine the attenuation correction by selecting the soil type and nuclide distribution type: recent (surface) sediments, older (washed-in) sediments, or natural (uniform) sediments. Energy and peak shape calibration are performed using multiline sources and can be automated. If you use ISOTOPIC, there are no unexpected detector calibration costs.

    Multiple measurements of a single container
    When measuring any large waste container, it is common to take multiple measurements from different directions to ensure results are obtained. If only one hardware system is available, measurements can be completed sequentially, or if multiple sets of hardware are available, measurements can be completed simultaneously. ISOTOPIC can automatically combine the results based on a user-defined weighted average. When using multiple detectors at the same time, the real-time spectrum of each detector can be displayed simultaneously on the screen to ensure data accuracy.

    Standard and custom reports
    ISOTOPIC offers flexible reporting within a standard product. All changeable parameters can be included in the standard output report. Analysis results are stored in an MS Access compatible database for easy printing or export for further processing into summary reports. Customized reports can be generated using Crystal Reports.

    Hardware compatibility
    Like all ORTEC CONNECTIONS application software products, ISOTOPIC is compatible with all ORTEC MCA hardware. In particular, it is ideal for use with the IDM-200-V, a complete rugged portable HPGe spectrometer system that does not require the use of liquid nitrogen.

    Support system integrators
    System integrators are often required to develop automated systems in which the details of hardware control and analysis are largely hidden from human operators beneath a software layer designed to provide a simplified user interface and/or allow for unattended operation. The standard user documentation set contains extensive documentation that uses example material to illustrate how to control the analysis engine from the command line. Analysis parameters and analysis results will be saved to an ACCESS compatible database. It provides all required file structure information, including ISOTOPIC database file structure. The spectrum or "SPC" file structure is provided in a separate accompanying manual.

    ORTEC hardware control is implemented through the so-called UMCBI, which provides a common API for all supported spectrum hardware. A Programmer's Toolkit is available as an option to provide the system integrator with instructions on how to easily control the MCA hardware from a program developed by him/herself. Typically, a basic ISOTOPIC program is used to set up the system hardware and calibrate, and then the integrator's application will control the system during the regular operating cycle. With these tools and the level of documentation provided, system integrators can easily develop complex measurement systems.

    Use ISOTOPIC
    ISOTOPIC has two modes: Administrator and Operator. Operators only need to make choices from a minimal subset of system options defined by the administrator. Administrator mode is used to define the actions an operator is allowed to perform. A wizard will guide the administrator in setting up the operator program. Wizards display parameters on logically grouped screens and emphasize the feasibility of the method.

    Administrator/operator partitioning enables even semi-skilled operators to collect good data in the field while reducing wasted duplication time (lower cost per measurement project). Of course, skilled users can choose to run both modes.

    Administrators can calibrate the system, create libraries, define sample geometries, matrices, collimators, and other features for later use by operators. Administrators can also define the functions that operators are allowed to access.

    The operator home screen is determined by the permissions granted by the administrator and is much simpler than the administrator screen. In daily use, for container analysis, the operator only needs to start acquisition, select a configuration (the standard container configuration), and enter "log data" such as container ID, type, weight and key measurements (such as detector-to-vessel distance).

    Standard container configurations and collimator configurations are defined and specified by the administrator. Container configurations include default dimensions, materials, and substrate details. The operator can specify and recall any number of these configurations when needed.

    Analysis tools
    Interactive results graph
    Once the analysis is complete, the operator can optimize the results by adjusting vessel/matrix physical parameters (such as matrix density or vessel wall thickness) by using the nuclide map.

    The graph shows the percentage difference between the corrected measured activity and the calculated reference peak activity for each nuclide. The administrator can select the reference peak. Operators can optimize the analysis, adjusting the vessel, matrix and uranium weight fraction to optimize results. If the points from a multimodal nuclide are normally distributed around the "zero line", this means a good result. When analyzing uranium, if U-235 enrichment is known, this value can be entered to more accurately calculate U-238 and U-234 values ​​in samples containing weak uranium activity. This method allows homogeneous and inhomogeneous samples to be analyzed with greater precision. For parcels with uneven material distribution, the user will have parameter combinations that will flatten some nuclide activity maps. This plot, along with the spectrum, can form part of the output report.

    Field of view calculator
    The detector field of view is an important parameter in measurements. Software algorithms "correct" or adjust based on what is "seen" in the collimator's field of view to analyze the contents of the entire container. In general, the field of view is chosen so that it is filled by the bin, being further away from this will reduce the signal-to-noise ratio in the spectrum, and being closer to this will cause the measurements to be more susceptible to local inhomogeneities (the effects can be further reduced by taking multiple measurements in different directions). A convenient field of view calculator allows the operator to evaluate which part of the container is actually within the collimated detector's field of view.

    report
    Once fine-tuning is complete, the operator can select reports for each nuclide showing activity and weight. These results are then printed and archived. Report files can be written as a database summary or a full report, which will show all input and correction information. Use the report generator option to generate custom reports. Component tables of error estimates can be used to help reduce the overall uncertainty, for example, by extending the counting time or repositioning the detector. Users will also be warned if any corrections appear to be too large. Calculate the minimum detectable activity (MDA) for each nuclide. Multiple measurements of activity, grams of U or Pu, or MDA may be reported as a weighted average. Weighting is user-definable.

    accuracy of results
    The basic assumption for a single measurement is that the entire object contains the same matrix and specific activity as the volume of the part being measured. Inaccuracies due to this incorrect assumption can be reduced by taking multiple measurements from different points on the object's surface and comparing the similarities. These comparisons can be used to develop measurement strategies for individual objects that reduce such systematic errors. If required, ISOTOPIC can provide a weighted average report including the relevant minimum detectable activity.

    Overall, the main influencing factors on the accuracy of the results are: statistical and counting times, calibration uncertainty, the number of repeated measurements made on a single object (random uncertainty), inhomogeneities in the matrix density and nuclide distribution and the number of measurements made on a single object from different directions (systematic errors).

    An accuracy range of 10 to 50% should be considered representative, with smaller ranges for well-defined geometries in homogeneous and lightweight matrices.

    Analysis Library Manager
    ISOTOPIC includes a comprehensive library editor for building custom analysis libraries. The editor allows the operator to cut and paste nuclides and peaks from the main library, add identification markers (single escape peaks, X-ray or other) and analysis (keyline or exclusion from activity calculations) to individual peaks, and save the library under any name. It also integrates the complete Nuclide Navigator library tool. ISOTOPIC will use Nuclide Navigator, read the Nuclide Navigator library in Microsoft Access database format (no conversion required), and save the library in database format for use by Nuclide Navigator.

    quality assurance
    ISOTOPIC's quality assurance meets the requirements of ANSI N13.30. For each detector, the following is monitored:

    • Detector total background
    • Total (decay-corrected) activity of all calibration nuclides
    • Average FWHM ratio (spectrum to calibration standard)
    • Average FW1/10M ratio (spectrum to calibration standard)
    • Average peak offset from library value
    • actual peak center energy

    Calculation details

    A review of isotope patterning methods for containers
    The activity of the isotope in the container is given by:

     

    Among them

    Aisotope = Reported isotope activity (Bq/μCi)。

    PAmeas = The measured peak area count rate (c/s) of the isotope reference gamma ray. This quantity can be determined directly from the spectrum and acquisition live time. ORTEC's ZDT dead time correction algorithm is very useful if short half-life isotopes are present or if there are rapid changes in sample activity in flowing samples.

    CFitem = Container, matrix and sample self-attenuation correction factors. ISOTOPIC calculates these data based on the physical data provided in the configuration.

    CFcol=Collimator correction factor. Some of the gamma rays will penetrate the collimator surrounding the germanium detector. The collimator correction factor depends largely on the diameter of the collimator, the depth of collimation and the wall thickness of the collimator as well as the angle of the radiation and its energy.

    The collimator correction factor can be determined by first calculating the portion of the activity that is not obscured by the collimator and then calculating the length of the remaining activity that penetrates the collimator. This is determined for each voxel of the item being measured.

    If there is no collimator, set to 1.

    BRray = Gamma ray branching ratio. This information is contained in nuclide libraries.

    det = detector efficiency (cps/Bq, μCi) measured using a NIST traceable point source. A typical calibration distance is 30 cm, at which distance the detector and source can be viewed as point objects. At close range, detector length and diameter dimensions cannot be ignored. By providing these dimensions during the calibration process, simple "point detector" assumptions can be corrected automatically. Correction of closed geometries is described in the ISOTOPIC Administrator's Manual 1.

    When it is necessary to report the gram quantity of an isotopeMassisotope, these are given by:


    Among them
    N = number of atoms of the reporting isotope.
    λisotope = reports the decay constant of the isotope (sec–1).
    At = atomic number of the isotope being measured (g/Av).
    Av = Avogadro's constant.

    Average the results of multiple measurements
    After multiple measurements are combined, a weighted average can be calculated according to the following equation:

    Aaverage = ∑ Ai wi/∑wi

    Among them
    Ai = Result for each activity (gram or MDA).
    wi = user-defined weighting factor.

    Soil
    Specific activity A (Bq/m2 or Bq/g) is related to the net peak count rate Nf:

    Among them
    Nf /N0 = angular correction factor of the detector at that energy for a given source distribution in the soil.
    N0 /Φ = peak count rate per unit of uncollision flux for a parallel gamma-ray beam of peak energy incident perpendicular to the detector plane (cpm/γ s–1)。
    Φ/A = total uncollided flux reaching the detector at peak energy per unit inventory or nuclide concentration in the soil (γ cm–2 s–1)  or (γ g–1 s–1)。

    Methods for estimating calibration factors use information about the detector and the distribution of the radionuclides being measured:

    • Detector efficiency (expressed as %)
    • Detector direction (up or down)
    • Detector aspect ratio (calculated as crystal length/crystal diameter)
    • Sedimentary profile parameter α/ρ value

    For all natural emitters, α/ρ is assumed to be 0 (uniform distribution). For settlement on undisturbed soil, α/ρ is assumed to be infinite (for surface distribution only).

    The Beck method is applied in ISOTOPIC by calculating the value of each calibration parameter. Each gamma ray will be calculated for all identified nuclides.
    ________________________________________

    1Hagenauer, R.C., “Nondestructive testing and quantitative analysis of poorly characterized radioisotopes,” Proceedings of the Fourth Conference on Nondestructive Testing and Nondestructive Waste Characterization, Salt Lake City, 1995.

    2 H. L. Beck et al., "In situ Ge(Li) and NaI(Tl) gamma-ray spectroscopic measurements," U.S. Department of Energy, Environmental Measurement Laboratory, HASL-258, September (1972).

    3 I. K. Helfer and K. M. Miller, "Calibration factors for Ge detectors for in-situ spectrometry", Health Physics, Vol. 55, No. 1, pp. 15-29 (1988).

    42012 NPL Nuclear Industry Proficiency Test Exercise. NPL Report IR 30 2013 (UK National Physical Laboratory). The ORTEC system is numbered 9.

    5 For soil characterization in M-1 mode, it is recommended to use HPGe with crystal length/diameter in the range of 0.5 to 1.3. 80% of HPGe detectors meet this standard. ORTEC PROFILE M series detectors are ideally suited for this and ISOTOPIC vessel measurements. Specifications-

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    General specifications
    Acquisition control and quantitative analysis functions are combined in a compact package for PC-based in-situ gamma spectroscopy measurement systems to determine the radioactivity content of containers, objects, surfaces and soils.

    operating system
    Windows 7 64-bit hardware compatibility applies to all ORTEC instruments using USB and TCP/IP connectivity protocols. Windows 7 and XP 32-bit operating systems also support these instruments as well as other legacy hardware.

    Spectral measurement hardware support
    It is recommended to use ISOTOPIC in conjunction with the ORTEC IDM-V-200 integrated HPGe spectrometer. But it is compatible with all ORTEC MCBs (past and present) and all other devices supported by ORTEC CONNECTIONS. Supports advanced operations (requires hardware support): amplifier gain/shaping control, automatic PZ, "Optimize" and InSight™ modes, digiDART field mode, graphical settings for MCB spectrum stabilizer and statistical uncertainty peaking. It is generally recommended to use the IDM-200-V for on-site measurements.

    Supported file formats
    ORTEC .SPC and .CHN as well as ASCII ".SPE" are standard formats in file saving, recall and comparison functions. Other file formats can be imported using the A49-B32 Data Master.

    Quantitative spectral analysis methods

    peak search
    Peak searches by library direction for specified nuclides and Mariscotti peak searches for unspecified nuclides, both main and supplementary ("suspicious") libraries were used.

    Interactive batch sample parameter adjustment
    Interactive matrix and container adjustments and automatic attenuation correction for new matrices. Easy-to-use graphical display of relevant analysis results showing matrix.

    Deconvolution method
    Both peak finders and libraries can be used to guide the deconvolution process. Where possible, energies/channels are automatically recalibrated based on identified peaks.

    Select detection limit format

    • ORTEC Tradition
    • ORTEC critical level
    • No MDA (report zero if below MDA)
    • KTA rules
    • Detection limit 2 sigma - Japan
    • Detection limit 3 sigma - Japan
    • Curie detection limit
    • RISO MDA
    • ORTEC LLD
    • Peak area
    • Air Monitoring - Gimrad Method
    • Regulatory Guidance 4.16 Method
    • Counting Laboratory - USA
    • DIN 25 482.5 detection limit
    • DIN 25 482.5 detection limit
    • GTN5/CEA/EDF (France)
    • Nureg 0472

    decay correction

    • Backward or forward decay correction for any date/time

    Spectral correction

    • Peak background correction
    • Random summation (high rate count loss)
    • Library-based peak interference correction

    report
    Select ORTEC standard reporting options:

    • Print directly
    • Automatically write to database
    • Output in Crystal Report format
    • Report in HTML format. From there it can be saved as a disk file.

    Calibration

    energy calibration

    • Multipoint, energy and FWHM quadratic
    • Automatic energy calibration (No. 6,006,162)

    Semi-empirical efficiency calibration fitting options:

    isotope pattern
    Establish a point source calibration by one of the following methods:

    • Single function polynomial (x point)
    • Interpolation above and below the "knee point"
    • User sets the "inflection point" above or below the quadratic
    • User sets the "knee" above or below the linear

    The point source calibration is extrapolated to the case of the substrate physical geometry via point source kernel calculations within the program.

    Infinite planar mode (for soil and surface: non-collimated detector)
    The Beck21 meter method is scalable to large detector size 3 and is used by the U.S. Department of Energy's Environmental Measurement Laboratory (EML). The EML method generates efficiency curves based on detector size and IEEE efficiency values. Soil density and attenuation are specified in user-editable α/ρ files.

    soil attenuation factor
    In soil, attenuation depends on soil thickness and density, which is modeled by the parameter α/ρ (where α is the reciprocal of the relaxation length, defined as the soil thickness required to reduce the flux at a specific energy by a factor e, and ρ is the soil density in gm/cc). For surface distributions, α/ρ is infinite, while for uniform (natural emitter) distributions, α/ρ is 0. α/ρ values ​​in the range of 0.05 to 0.5 were found to accurately describe the true settlement distribution, with longer settlements represented by smaller α/ρ values.

    The α/ρ values are related to a specific nuclide and are stored in a table that can be edited by the user to reflect the measurement conditions.

  • Ordering information +


    Model

    Description

    ISOPLUS-BW

    ISOTOPICAdvanced Gamma Ray Waste Measurement Analysis Software

    ISOPLUS-GW

    ISOTOPICDocumentation

    ISOPLUS-NW

    ISOTOPICnetwork copy

    ISOPLUS-UW

    updated toISOTOPIC

    ISOPLUS-2YW

    ISOTOPICof2Annual renewal subscription

    ISOPLUS-3YW

    ISOTOPICof3Annual renewal subscription

    ISOPLUS-4YW

    ISOTOPICof4Annual renewal subscription

    ISOPLUS-5YW

    ISOTOPICof5Annual renewal subscription

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