Introduction
A 1000 MWe nuclear power unit will produce approximately 13,000 m3 of low-level and intermediate-level radioactive waste (LILW) [1] after 60 years of operation. After solidification or compression, this waste is prepared in 200 L and 400 L drums [2], with a total volume of approximately 3000 m3. An International Atomic Energy Agency (IAEA) technical report [3] stated that to ensure safety within the entire LILW management life cycle, the LILW must be characterized. At the same time, according to the IAEA safety standard [1], the disposal depths of LILW for different activity ranges differ, and thus quantitative analysis of LILW is necessary. Because destructive methods and time-consuming drilling are necessary to reopen a container [4], a nondestructive assay (NDA) is generally the best choice. Some important LILW nuclides include alpha-emitting nuclides (most actinides and transuranic nuclides) and beta-emitting nuclides (C-14, Ni-63), which cannot be used for NDA. Thus, these nuclides are called difficult-to-measure (DTM). According to the International Organization for Standardization [5], by performing gamma scanning on easy-to-measure nuclides (also called key nuclides) such as Cs-137 and Co-60, it is possible to establish a scaling factor between key nuclides and DTM and calculate the activity of the DTM. Therefore, gamma-ray scanning is required to characterize LILW.
According to the American Society for Testing and Materials (ASTM) Standard Guide [6], NDA methods include segmented gamma scanning (SGS) [7] and tomographic gamma scanning (TGS). TGS is particularly well-suited for items with heterogeneous matrix materials and non-uniform radioisotope distributions. Some studies have been conducted on SGS and TGS [8–18]. For both SGS and TGS, it is necessary to use gamma ray spectroscopy to conduct qualitative and quantitative analyses of the LILW gamma spectrum. Owing to the diverse range of nuclides in LILW and the variations between waste streams [19,20], identifying nuclides can be challenging. Therefore, high-resolution high purity germanium (HPGe) gamma ray spectrometry is the optimal method for LILW measurement [21–25].
The spectrum measured by an HPGe detector must be analyzed to obtain the counts of gamma rays with different energies. The main steps of the spectrum analysis method [26] include smoothing, background subtraction [27], peak searching, and calculation of the peak area. Nuclide identification relies on the process of peak searching. Currently, the most mature peak-searching method is the derivative method proposed by Mariscotti [28]. GammaVision (GV) [29] and Genie 2000 [30] have adopted this method. Because of the limited peak-searching ability of the derivative method, it is necessary to establish a nuclide library to assist in identifying overlapping peaks composed of two full-energy peaks that are very close to each other. This method assumes that all gamma rays in the nuclide library are present in the spectrum, and thus it attempts to fit the peaks for every gamma energy listed in the library. Therefore, for the same peak, different results are often obtained with different nuclide libraries. For example, common LILW nuclides include Cs-137 emitting 662 keV and Ag-110m emitting 658 keV. The nuclide composition of the LILW before measurement is not accurately known. For the same full-energy peak of 662 keV, if only 662 keV is defined in the nuclide library, the quantitative analysis result is accurate. However, if both 658 keV and 662 keV are provided in the nuclide library, the report will provide a full-energy peak count of 658 keV. This results in misidentification of the nuclide. At the same time, the calculated 662 keV peak area decreases, resulting in inaccurate activity calculations, which is a potential safety hazard for the disposal of LILW. The IAEA report [29] also noted that this method requires the availability of good nuclear data libraries. Other peak-finding methods include the IF function method [31], zero-area fold-in method [32], Gaussian product function method [33], covariance method [34], continuous wavelet transform (CWT) method [35], and neural network method [36]. Compared with the derivative method, these methods are an improvement; however, they still require auxiliary identification of the nuclide library.
In this study, to solve the problem of uncertainty in the nuclide library causing instability in the analysis results for LILW spectra, a novel spectrum analysis method is proposed to reduce this uncertainty and improve accuracy. For each step in the spectral analysis process, the overlapping peak decomposition process does not rely on the assistance of the nuclide library. This study improves the accuracy of LILW measurements and provides key technical support for the safe disposal of LILW.
Materials and Methods
Analysis method
Traditional spectral analysis method
In traditional spectral analysis methods, there are problems with each of the basic steps. When smoothing the spectrum according to a five-point smoothing algorithm [37], the processing causes the maximum value of the peak to decrease each time, and the counts on both sides of the bottom of the peak increase. Thus, the calculation of the peak area is inaccurate. At the same time, it is difficult to identify the nuclide because of the changes in the peak shape.
According to the GammaVision user manual [37], background subtraction methods include the straight-line, stepped, and parabolic background methods [38]. These methods provide only rough approximations of the background, thereby increasing the peak area calculation error. At the same time, Miroslav [39] showed that the parabolic background had very poor robustness [38].
The peak search method was proposed by Mariscotti [28]. This method has a limited ability to separate overlapping peaks [32], resulting in inaccurate nuclide identification; furthermore, it is highly susceptible to noise. Thus, it is necessary to smooth the spectrum multiple times before searching for the peak, which leads to changes in the peak shape and increases the error in the peak area calculation.
The final step is the quantitative analysis of overlapping peaks. In traditional methods, a preliminary library-based peak search of the spectrum is performed. The analysis assumes that all of the gamma rays listed in the library are present in the spectrum; therefore, an attempt is made to fit a peak at every gamma energy listed in the library. Therefore, as reported in Ref. [40], if the nuclide library is inaccurate, it will increase the error in the spectral analysis results.
Spectral analysis method proposed in this study
According to Knoll [41] and the IEC international standard [42], for a single overlapping peak composed of multiple full-energy peaks with similar energies, the only method to conduct an analysis is through deconvolution. The deconvolution method can be used to establish the relationship between the incident gamma ray spectrum and the energy deposition spectrum using the response function of the detector, as follows [43]:
For
For a discrete system,
The solution to Eq. (1) is an ill-posed problem. According to Miroslav [46], iterative regularization has strong positive constraints and noise-suppression capabilities. Currently, the most effective method for gamma spectrum analysis is the boosted traditional iterative algorithm [47]. In this study, a boosted maximum-likelihood expectation-maximization algorithm [48] was used.
Through this deconvolution process, the deposition spectrum of gamma rays with different energies can be converted into the incident
Background subtraction methods include the linear method [30], approximate physical models for the background, the polynomial method [49], digital filtering [50], peak clipping [38], fast Fourier transform [51], and the sensitive nonlinear iterative peak (SNIP) method[52]. Among these methods, the most effective background subtraction method is the improved SNIP method, i.e., adaptive SNIP [39].
The basic concept of the adaptive SNIP method is to divide the energy spectrum into two regions: the region where the peak is located, and the region where there is no peak. For the peak area, the SNIP filter is used for background subtraction, and for the non-peak area, all of the gamma counts are regarded as the background. Therefore, the problem is to determine how to calculate the peak position, peak width, and selection of the clipping filter.
This study proposes a calculation method for peak position identification based on CWT. The wavelet transform of a signal
The correct choice of wavelet is the key to obtaining the results of the spectrum analysis. As the full-energy peak of the spectrum is a Gaussian function, a Mexican hat wavelet (Mexh) is selected because its shape is similar to that of a Gaussian peak. The definition of Mexh is given as follows [54]:
By analyzing the scalogram, the position information of the peak can be obtained. The next step is to calculate the widths of the peaks based on their positions.
The peak width can be obtained directly from the scalogram obtained with Eq. (4), but because the peak widths of different scales are different, this method has large errors [55]. The peak width can be calculated using a Gaussian product function [33], but it is highly susceptible to noise interference. The width can also be determined from the shapes of the peaks using function fitting [56]. This approach is also difficult to use because the number of singlets comprising the overlapping peaks is unknown. In Refs. [55] and [56], a method for calculating the peak width based on the second convolution of the Gaussian first derivative was proposed.
The expression for the full-energy peak is as follows [57]:
The calculation result for the second convolution of the Gaussian first-order derivative of Eq. (7) is expressed as follows [54]:
Using Eq. (8), the crossing point of the zero value can be determined as follows [54]:
However, other studies have shown that this method is not suitable for calculating overlapping peak widths that contain too many full-energy peaks [39]. Therefore, in this study, we propose an improved method.
For Eq. (8), the calculation of the width of the peak requires the determination of the parameter
Next, the background of the peak area must be removed. For the SNIP method, first, to compress the dynamic range of each channel count in the spectrum to speed up the iteration, a linear least-squares operator is applied to the spectrum data [52]:
For the count
For the adaptive SNIP [39], the spectrum is divided into two areas: the non-peak and peak areas. In the non-peak region, all of the gamma counts are the background. In the peak region, the background is subtracted using the traditional SNIP method. Eq. (11) represents a second-order filter that can effectively remove the linear background. To solve the problem of the inability to subtract the background at the Compton edge for the full-energy peak as described in Sect. 2.1.1, a novel method is proposed.
Because the Compton edge can be approximated by a cubic function to some extent, and a cubic function can be removed by a fourth-order clipping filter, a fourth-order clipping filter is proposed for background subtraction in the peak area. The parameters of the equation were derived from Pascal’s triangle [59] formula. The fourth-order clipping filter is defined as follows:
Through the peak searching and peak width calculations described above, the spectrum can be divided into peak and non-peak areas, which are combined with a fourth-order clipping filter in the peak area. Thus, effective subtraction of the background is realized and the net spectrum is obtained.
During the smoothing process in the traditional method, the peak count will decrease. This study uses a low-pass filter [52] to smooth the spectrum and effectively solve this problem.
Experimental condition
Experimental configuration
The HPGe detector was an Integrated Cryocooling System produced by ORTEC. Its relative efficiency at 1.33 MeV is 30%. The detector crystal has a diameter of 51.8 mm and length of 60.9 mm. The cold finger has a diameter of 8.7 mm and a length of 38.2 mm. The dead layer at the front end of the crystal has a thickness of 0.03 mm. The DSPEC-50 multi-channel analyzer was manufactured by ORTEC.
GV 6.08 spectral analysis software was used. The analysis parameters of GV included the calibration (.CLB) file, peak background correction (.PBC) file, and nuclide library (.LIB) file; the analysis program was WAN32. The standard area of the peak was calculated by selecting the region of interest (ROI) in the GV; the peak width was three FWHM.
The experiments were conducted using the Tomographic Gamma System (SJTU-TGS), which was independently developed by Shanghai Jiao Tong University, as shown in Fig. 1(a). The detector was equipped with a lead collimator (liftable). The exterior dimensions of the collimator and collimation window were 25 cm (L)× 36 cm (W)× 40 cm (H) and 9 cm (L)× 20 cm (W)× 25 cm (H), respectively, and the thickness of the lead was 8 cm. The distance between the detector surface and drum center was 74 cm. The system had a liftable transmission source storage device. The waste drum could be moved and rotated. Therefore, the measurement system had detection functions of SGS and TGS and could also meet the requirements of 200 L and 400 L waste drums at the same time.
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Source test conditions
To verify the accuracy of the spectral analysis of the different nuclides, the radioactive sources used were standard point sources: monoenergetic gamma ray nuclide Cs-137 [60] (7.86×105 Bq) and multi-energy gamma-ray nuclide Eu-152 [61] (2.74×106 Bq).
To obtain the spectrum of the radioactive source attenuated by different densities, the radioactive source was placed in a 200 L drum filled with different materials for measurement. The materials used in the drum were air (the empty drum), water (1 g/cm3), and sand (1.6 g/cm3).
To explore the influence of different nuclide libraries on the GV analysis results, multiple verification experiments were conducted on 200 L drums. The radioactive source, Cs-137, was placed at different positions in the drum, as shown in Fig. 2, and the drum was not filled with material. The time for each measurement was 10 min.
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SGS experiment
The purpose of spectral analysis is to measure the activity of LILW. Therefore, a 200 L standard drum was employed. The material in the drum was water. Cs-137 was placed at radii of 0, 6.25, 11.25, 16.25, 21.25, and 26.25 cm, and the height was 42.5 cm (half the height of the drum). SGS [7,16] was used for activity reconstruction based on the SJTU-TGS system.
The same standard drum was used for activity reconstruction with the Canberra SGS System [25], as shown in Fig. 1(b). The aim of this study was to compare and analyze the activity measurement results of the two systems. The spectroscopy software in the Canberra SGS System is Genie 2000 [30], and the software for measurement activity is NDA2000 [62]. To control for the variables, the SJTU-TGS System adopts the SGS method described in NDA2000 (refer to Refs. [7] and [61]). The efficiency calibration method of the SJTU-TGS system adopts the method described by Qian [12], which meets the ASTM standards [63]. Because the material was water, this was an easy task for efficient calibration. It was assumed that any calibration method would provide relatively consistent results. During the gamma scanning, the drum was vertically divided into eight layers, and the lifetime of each layer was 1 min. Considering the dead time and moving time of the detector, the measurement time for a drum was approximately 10 min, which was within the measurement time range for 200 L drums in nuclear power plants. The only difference is that the SJTU-TGS System adopted the novel spectral analysis method proposed in this study. For the Canberra SGS System according to Genie 2000, its method was very close to GV, and thus it represented the traditional spectrum analysis method.
Experiments and Discussion
The verification experiments for the spectral analysis method included the following parts: a preliminary verification experiment for a single nuclide, instability experiments for the nuclide library, activity measurement comparison experiments for the standard drum, and overlapping peak simulation spectrum experiments.
Preliminary verification experiment for a single nuclide
Spectra of monoenergetic gamma ray nuclides
The original spectra of the Cs-137 nuclide without attenuation and those attenuated by water and sand are shown in Fig. 3(a); the normalized spectra are shown in Fig. 3 (b). The Compton plateau in the attenuated spectrum is significantly higher than that in the unattenuated spectrum. Three spectra were analyzed using the proposed method. For comparison, GV was used to establish an accurate nuclide library and the nuclide analysis results were obtained. The spectral analysis results obtained using different methods are shown in Fig. 4, and the quantitative results are presented in Table 1.
Material | Method | Standard peak area of ROI | Calculated peak area | Error |
---|---|---|---|---|
Air | GV | 54,226 | 55,676 | 2.4% |
Novel method | 52,895 | −2.71% | ||
Water | GV | 1084 | 1091 | 0.65% |
Novel method | 1065 | −1.75% | ||
Sand | GV | 978 | 1004 | 2.66% |
Novel method | 982 | 0.41% |
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As shown in Fig. 4, through the deconvolution process, the proposed method converted the number of full-energy peak channels into one channel, making it very easy to identify nuclides. The results in Table 1 indicate that because of the simple task of single-peak nuclide identification, the results were similar to those of GV, and the errors for both methods were less than 3%.
Spectra of multi-energy gamma ray nuclides
Because the nuclides in LILW generally emit multi-energy gamma rays, the Eu-152 spectrum was used for analysis and verification. The original spectrum of Eu-152 is shown in Fig. 5 (a). Gamma rays for eleven energies with the largest peak areas were selected for analysis. Because the energy resolution of HPGe is very good, the overall spectral lines appeared very clear. However, in the zoomed-in details, such as the 778.90 keV full-energy peak shown in Fig. 5 (a), the peak width was approximately 20 channels. The results of the spectral analysis using the novel method are shown in Fig. 5 (b). It can be observed that the gamma rays occupied only one channel, as seen in the zoomed-in details of the 778.90 keV full-energy peak. Thus, the accurate identification of nuclides could be realized.
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The results of the quantitative analysis of the novel method and GV are compared in Table 2. For the calculation errors of the full-energy peaks with different energies, the proposed method was more accurate, with a maximum error of 8.28%, whereas the maximum error of GV was 18.40%. This is because in the energy spectrum analysis process of GV, spectral smoothing is first performed, leading to some changes in the peak shape, and the peak area is calculated by fitting these peak shapes. Therefore for peaks with large statistical fluctuations, particularly those with relatively small peak areas, significant errors can be introduced during the smoothing and fitting processes. However, in the novel method, the full-energy peak is directly used to calculate the peak area during the process of deconvolution; thus, there is almost no significant deviation in the calculation of the peak area. From the perspective of the mean error (average error from all the peaks), GV has an error of 5.43%, whereas the novel method has an error of 3.89%.
Energy | Standard peak area | Calculated peak area (GV) | Error (GV)(%) | Calculated peak area (novel method) | Error (novel method)(%) |
---|---|---|---|---|---|
121.78 | 47,650 | 48,026 | 0.79 | 49,262 | 3.38 |
244.70 | 10,908 | 10,844 | –0.59 | 11,115 | 1.90 |
344.28 | 30,823 | 30,083 | –2.40 | 31,042 | 0.71 |
411.11 | 2283 | 2703 | 18.40 | 2401 | 5.17 |
443.97 | 2873 | 2987 | 3.97 | 3111 | 8.28 |
778.90 | 7794 | 8057 | 3.37 | 8047 | 3.25 |
867.37 | 2177 | 2456 | 12.82 | 2214 | 1.70 |
964.08 | 7377 | 7497 | 1.63 | 7811 | 5.88 |
1085.87 | 4760 | 5235 | 9.98 | 4953 | 4.05 |
1112.07 | 6369 | 6704 | 5.26 | 6589 | 3.45 |
1408.00 | 8122 | 8163 | 0.50 | 8528 | 5.00 |
Mean error | 5.43 | 3.89 |
Nuclide library instability experiments
These GV analysis results were based on an accurate nuclide library. However, in practical applications, it is generally difficult to make an accurate judgment regarding the suitability of the nuclide library. Therefore, for the same Cs-137 (662 keV) spectrum attenuated by sand, different nuclide libraries were used to analyze the GV results. Analytical results are also provided for this novel method, which does not require the establishment of a nuclide library. Because Ag-110m is the most common corrosion activation product in LILW and its gamma emission of 658 keV is close to that of Cs-137, the nuclide library settings were as follows: Cs-137, Cs-137+Ag-110m, and Ag-110m. The GV analysis results are presented in Fig. 6 and Table 3.
Number | Nuclide library (GV) | Standard peak area | Calculated peak area (GV) | Error (GV) | Calculated peak area (novel method) | Error (novel method) |
---|---|---|---|---|---|---|
1 | Cs-137 | 978 | 1004 | 2.7% | 982 | 0.4% |
2 | Cs-137+Ag-110m | 662 | 32.3% | 982 | 0.4% | |
3 | Ag-110m | - | - | 982 | 0.4% |
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As shown in Fig. 6, for the Cs-137 spectrum, if only Cs-137 was included in the nuclide library, the analysis result was accurate and the peak area error was only 2.7%. However, when Ag-110m was added to the nuclide library, a peak area of Ag-110m was obtained based on the spectral analysis mechanism; in other words, Gaussian functions with energies of 658 and 662 keV fit the full-energy peak of Cs-137. Therefore, the areas of the full-energy peaks of the two energies could be obtained, and thus the error of the peak area of Cs-137 increased to 32.3%. In the absence of Cs-137 in the nuclide library, the result did not provide a count of Cs-137; in other words, different nuclide libraries yielded completely different analytical results. By assuming the presence of a peak a priori, GV was “forced” to calculate the properties of the peak. This finding was consistent with the conclusions of Santoro [40]. Because the novel method does not require a nuclide library, the error in the analysis result was stable at 0.4%.
To further explore the influence of different nuclide libraries on the GV analysis results, verification experiments were carried out on 200 L drums, as shown in Fig. 2. For the nuclide library setting of the GV, in addition to Cs-137 (662 keV) and Cs-137+Ag-110m (662 keV + 628 keV), an artificial nuclide library was used with a composition of 662, 661, 660, 659, and 658 keV. The results of the spectral analyses with different methods are shown in Fig. 7, where the x-axis represents the identification number of the radiation source at different positions inside the 200 L drum. The analysis results of the novel method and the GV based on an accurate nuclide library were similar. The average relative error of the novel method was 3.3%, and that of GV was 3.4%. However, when the GV nuclide library consisted of two gamma energies, the 662 keV peak was fitted into two peaks, and thus the average error of the 662 keV peak was 38.3%. When the nuclide library consisted of five gamma energies, the 662 keV peak had the worst average error of 48.3% because 662 keV was “split” into five overlapping peaks.
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Activity reconstruction for a 200 L drum
For the 200 L standard drum, the SGS activity reconstruction results using the SJTU-TGS and Canberra SGS systems are shown in Fig. 8.
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For the two systems, except for the spectral analysis method, the other methods are basically the same. Therefore, theoretically, the activity reconstruction error primarily reflects the error of the spectral analysis method. As shown in Fig. 8, when the radius was relatively small, the measured value was low. As the radius increased, the measured value also increased. Because the SGS method was aimed at LILW in which the matrix and nuclides are uniformly distributed, the object of efficiency calibration was a uniform volume source. The Cs-137 source at different positions in this experiment was categorized as a situation in which the distribution of nuclides was extremely uneven, which does not satisfy the basic conditions of SGS. Thus, relatively large measurement errors inevitably occurred. For non-uniform cases, SGS can reach a maximum measurement error of more than 500% [64]. Therefore, when the radius of the source is small, the value of the efficiency calibration is too large and the measured value is too small. In theory, for the SGS method, there is generally an equivalent radius at the position of 0.7–0.8 R (R is the radius of the drum) [15,16], and the actual efficiency value at this position is close to the efficiency of the uniform source value. As a result, better measurement results can theoretically be obtained. Therefore, for the SJTU-TGS System, when the radius was 21.25 cm, it was close to the equivalent radius, and the spectral analysis results were relatively accurate. Therefore, the error was only 2.4%, whereas for the Canberra SGS System, the smallest error was 12.9%. To some extent, this reflects the accuracy of the spectrum analysis.
Analysis of overlapping peaks
Verification of the accuracy of the Monte Carlo simulation method
The types of nuclides in LILW are complex, and it is difficult to obtain different overlapping peaks experimentally to verify the spectral analysis method. Therefore, a Monte Carlo simulation was used in this study to simulate the process of measuring the radioactive source with an HPGe detector. A geometric model was constructed using the Geant4 tool [65,66]. According to the certificate of calibration (SRS number: 116230 and product code: 8403-GF-PNT) corresponding to the HPGe detector provided by ORTEC, the hybrid source (a point source in tape in a 2-inch aluminum ring) was placed horizontally 30 cm from the front end of the detector, and the detection efficiency curve was obtained experimentally. A comparison between the Monte Carlo simulation efficiency [67–70] and the experimental efficiency [71] is shown in Fig. 9(a). Except for the relative error of the full-energy peak efficiency at an extremely low energy (46.52 keV), which was 9.89%, all of other calculation errors were less than 5%.
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The Cs-137 spectrum experiment was conducted according to the measurement standard requirements of ANSI [72] and IEEE [73]. The collected full-energy peak count exceeded 20,000. The gamma count of the environmental background within the same measurement time was subtracted using the channel-by-channel method to obtain the net spectrum. A comparison between the normalized spectrum of the experiment and the Monte Carlo simulation is shown in Fig. 9(b). In addition to certain statistical fluctuations in the experimental spectrum, the full-energy peak and Compton plateau were in good agreement, verifying the accuracy of the Monte Carlo simulations.
Spectral analysis of key LILW nuclide overlapping peaks
Based on the key nuclide types of the LILW provided by the Qinshan Nuclear Power Plant and through the comparison and analysis of nuclides and their characteristic energies, three nuclides with the closest characteristic energies were selected: Sb-125 (601 keV), Sb-124 (603 keV), and Cs-134 (605 keV).
Different peak area ratios were set for the compositions of the three overlapping peaks. Because the overlapping peaks are difficult to decompose, it is easier to identify the nuclide as a full-energy peak located in the middle channel of the overlapping peaks. Therefore, if the peak area at the middle energy is lower than that on both sides, thus forming a weak peak, it is easier to elucidate the performance of the spectral analysis methods. Therefore, three overlapping peaks were set with peak area ratios of 5:1:10, 10:1:20, and 20:1:40 for 601, 603, and 605 keV, respectively. For overlapping peaks with larger area ratios, because the activity calculated with this weak peak does not contribute significantly to the total activity of LILW and does not affect its final disposal, it was not necessary to continue studying these cases. At the same time, to illustrate the difficulty of identifying overlapping peaks, the CWT with the strongest performance in the traditional peak searching method was used for comparison. The results of the spectral analysis are shown in Fig. 10, and the quantitative results are summarized in Table 4.
Number | True value | Calculated value | ||||
---|---|---|---|---|---|---|
Nuclide | Energy (keV) | Peak area | Energy(keV) | Peak area | Peak area error (%) | |
(a) | Sb-125 | 601 | 109,278 | 601 | 108,969 | -0.28 |
Sb-124 | 603 | 21,920 | 603 | 22,026 | 0.48 | |
Cs-134 | 605 | 217,095 | 605 | 216,716 | -0.17 | |
(b) | Sb-125 | 601 | 217,958 | 601 | 217,486 | -0.22 |
Sb-124 | 603 | 21,920 | 603 | 22,297 | 1.72 | |
Cs-134 | 605 | 434,017 | 605 | 432,783 | -0.28 | |
(c) | Sb-125 | 601 | 438,854 | 601 | 437,810 | -0.24 |
Sb-124 | 603 | 21,920 | 603 | 22,653 | 3.34 | |
Cs-134 | 605 | 868,397 | 605 | 865,777 | -0.30 |
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As shown in Fig. 10(a), through the precise deconvolution process, the novel method decomposed the overlapping peaks into three incident spectra whose shape was a
As shown in Fig. 10(c), under the condition of a peak area ratio of 20:1:40, by zooming in on the details in the original spectrum, because the area ratio of the three full-energy peaks was very different, it was determined that the 603 keV full-energy peak in the middle was completely covered by the high-energy peaks on both sides. The 603 keV full-energy peak was submerged. In the CWT scalogram, the weak peak at 603 keV could not be identified, and only two strong peaks at 601 and 605 keV could be identified. With the novel method, accurate nuclide identification could still be achieved for overlapping peaks in such extreme cases. The largest area calculation error for the strong peak was −0.3%, whereas that for the weak peak was 3.34%.
As shown in Fig. 10, for overlapping peaks under some extreme conditions, it was difficult for CWT to achieve an accurate nuclide analysis. CWT in the novel method was used to determine the positions of the overlapping peaks and perform subsequent peak width IAEA calculations. At this point, it did not matter which nuclides constituted the overlapping peaks.
Conclusion
In LILW spectrum analysis using existing methods, uncertainty of the nuclide library causes instability in the analysis results and reduces the accuracy of activity reconstruction. To address this problem, this study proposes a novel spectral analysis method. Through standard source experiments, standard drum experiments, and Monte Carlo simulation experiments, the following conclusions are drawn:
1. The novel method and GV with an accurate nuclide library exhibited similar spectrum analysis capabilities, and the analysis errors were less than 3% for Cs-137 and 4% for Eu-152.
2. The novel method does not require a nuclide library, and the analysis results were more stable than those of GV, which showed significant errors and instability in peak area calculations.
3. The novel method could be applied to the activity measurement of LILW, and the reconstructed activity of Cs-137 was accurate, with an error of 2.4%, while the minimum measurement error of the Canberra system was 12.9%.
4. The novel method could quantitatively analyze all of the nuclides in LILW without a nuclide library. For overlapping peaks composed of peak area ratios of 5:1:10, 10:1:20, and 20:1:40, the nuclide could be accurately identified; the area calculation error of the strong peaks was less than 1%, and the error of the weak peaks was less than 4%.
This novel method can improve the accuracy and precision of LILW measurements, provide key technical support for the reasonable disposal of LILW, and ensure the safety of humans and the environment.
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