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Study on element detection and its correction in iron ore concentrate based on a prompt gamma neutron activation analysis system

ACCELERATOR, RAY AND APPLICATIONS

Study on element detection and its correction in iron ore concentrate based on a prompt gamma neutron activation analysis system

Long Zhao
Xu Xu
Jing-Bin Lu
Ya-Lin Gong
Xiang-Lin Li
Wei Zhang
Qing-Min Shang
Qing-Feng Song
Yan-Feng Li
Nuclear Science and TechniquesVol.30, No.4Article number 58Published in print 01 Apr 2019Available online 13 Mar 2019
43401

A prompt gamma neutron activation analysis (PGNAA) system was developed to detect the iron content of iron ore concentrate. Because of the self-absorption effect of gamma rays and neutrons, and the interference of chlorine in the neutron field, the linear relationship between the iron analytical coefficient and total iron content was poor, increasing the error in the quantitative analysis. To solve this problem, gamma-ray self-absorption compensation and a neutron field correction algorithm was proposed, and the experimental results have been corrected using this algorithm. The results show that the linear relationship between the iron analytical coefficient and total iron content was considerably improved after the correction. The linear correlation coefficients reached 0.99 or more.

Prompt gamma neutron activation analysisSelf-absorptionEnergy spectrumCompensationCorrectionIron ore concentrate

1 Introduction

Prompt gamma neutron activation analysis (PGNAA) is a form of rapid and non-contact multi-elemental analysis technique, which has been widely used for element detection and analysis in various fields, such as cement, coal, and mineral resource industries [1-15]. With real-time, online detection results from PGNAA, a factory can adjust the control parameters simultaneously, and hence, improve the product quality. The PGNAA technique is based on the detection of prompt gamma rays emitted through thermal neutron capture (nth, γ) or neutron inelastic scattering (n, n′γ) [1,2]. It can distinguish the elemental categories in the material from the characteristic γ-ray energy spectrum, as well as estimate the element content from the intensities of characteristic energy peaks in the spectrum [3,4]. PGNAA technology involves neutron moderation technology, characteristic gamma-ray energy spectrum technology, as well as the spectrum de-convolution technique [5-10]. At present, PGNAA technology is widely used to detect high contents of light elements or low contents of heavy elements in a sample, such as calcium, silicon, iron and aluminum in cement [1,4,12]. Owing to the self-shielding effect of gamma rays and neutrons in some heavy elements [16-20], which increases the error of PGNAA technology in the detection of heavy element concentrates, the applications of PGNAA technology using heavy elements is limited.

In the steel industry, the sintering process is quite sensitive to the iron ore concentrate grade, thus, real-time and accurate detection of the grade is very important to improve the sintering process and sinter quality. Here, a new correction algorithm, with gamma-ray self-absorption and neutron self-absorption considered, for the detection of iron ore concentrate grade by PGNAA is developed. By means of the new correction algorithm, the linear correlation between the iron analytical coefficient and the total iron content has been improved from 0.79747 to 0.99886, and the influence of chlorine in the sample on the detection error has been reduced as well. As a result, an effective and accurate real-time detection of the iron ore concentrate grade during the sintering process has been demonstrated based on PGNAA technique and the new correction algorithm.

2 Experiment

2.1 Equipment setup

A PGNAA was used to detect the iron content in iron ore concentrate in the experiment. Fig. 1 schematically shows the equipment setup [15]. Two 20 μg 252Cf neutron sources were placed in the source chamber. Two 5 inch×5 inch (diameter × height) NaI detectors were used as the prompt gamma-ray detector. The experimental equipment was produced by DFMC, which was suitable for a one-meter-wide belt. The spectrum acquisition time of each sample was set to 3600 seconds. Because of the strong shielding ability of iron on gamma rays, the characteristic gamma ray of a sample containing iron should have strong gamma-ray self-absorption [21]. To measure the self-attenuation degree of gamma rays, one gamma-ray attenuation degree detection system was installed after the PGNAA, which included a 137Cs gamma radiation source installed below the belt and a γ-ray detector installed above the belt, as shown in Figure 2.

Fig.1.
PGNAA device structure
pic
Fig. 2.
System structure diagram
pic
2.2 Sample preparation and experimental load

Six calibration samples and nine validation samples, with differing iron contents, were prepared for the experiment. Silicon, magnesium, calcium, and chlorine interference elements were added in sample 2-1#~2-9# to simulate a real test. The compositions of the calibration samples are shown in Table 1, and the composition of the verification samples are listed in Table 2.

Table 1
Chemical composition of calibration samples, wt(%) relative to dry material
Sample TFe SiO2 CaO MgO Cl Other
1-1# 46.34±0.16 9.19±0.08 9.8±0.07 4.98±0.1 1.22±0.09 8.61
1-2# 48.23±0.16 9.88±0.08 9.92±0.07 1.95±0.08 0.94±0.07 8.41
1-3# 50.75±0.16 8.34±0.08 8.14±0.06 2.62±0.08 0.51±0.04 7.89
1-4# 54.6±0.16 6.45±0.08 6.73±0.06 1.45±0.08 0.27±0.02 7.1
1-5# 52.85±0.16 6.89±0.08 5.54±0.06 3.36±0.08 0.69±0.05 8.02
1-6# 58.1±0.16 4.14±0.06 4.53±0.06 0.51±0.07 0.33±0.03 7.49
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TFe=total ferrous content
Table 2
Chemical composition of check samples, wt(%) relative to dry material
Sample TFe SiO2 CaO MgO Cl Other
2-1# 47.29±0.16 9.54±0.08 9.86±0.07 3.47±0.08 1.08±0.08 8.49
2-2# 49.49±0.16 9.11±0.08 9.03±0.07 2.29±0.08 0.73±0.05 8.14
2-3# 50.54±0.16 8.39±0.08 7.73±0.06 2.66±0.08 0.82±0.06 8.2
2-4# 52.68±0.16 7.4±0.08 7.44±0.06 2.04±0.08 0.39±0.03 7.47
2-5# 48.55±0.16 8.77±0.08 8.97±0.07 3.8±0.1 0.87±0.06 8.23
2-6# 51.8±0.16 7.62±0.08 6.84±0.06 2.99±0.08 0.6±0.04 7.95
2-7# 55.48±0.16 5.52±0.06 5.04±0.06 1.94±0.08 0.51±0.04 7.73
2-8# 53.73±0.16 6.67±0.08 6.14±0.06 2.41±0.08 0.48±0.04 7.54
2-9# 56.35±0.16 5.3±0.06 5.63±0.06 0.98±0.07 0.3±0.02 7.29
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TFe=total ferrous content

An inflection curve is observed for the analytical coefficient between the deconvolution coefficient of iron and the sample load owing to the gamma-ray self-attenuation effect, as shown in Figure 3. In Figure 3, the linear region is between 60 to 130 kg. To obtain more rational results, 110 kg was selected as the experimental load in this study.

Fig.3.
Analytic coefficients of iron with different loads
pic
2.3 Gamma-ray self-absorption correction

The following compensation formula [22] for gamma-ray self-absorption is used to correct for self-attenuation:

I0Ei=IEiexp(μmEiμ0ln(N N0))  (1 MeVEi10 MeV) (1)

where I0Ei is the energy spectrum without attenuation, IEi is energy spectrum obtained by the PGNAA detector, μmEi is the characteristic gamma-ray mass attenuation coefficient with energy Ei, μmEi is related to the atomic number of the material and the energy of the gamma ray, N is the detector count rate of the gamma-ray attenuation degree detection system when there is material on the belt, N0 is the detector count rate of the gamma-ray attenuation degree detection system with no material on the belt, μ0 is the mass attenuation coefficient of the 137Cs radioactive source with energy equal to 0.662 MeV.

The linear absorption coefficient, μ, of the material is defined as follows:

μ=Niσiγ   i=Ca,Si,O,Mg,Cl,Fe (2)

where Ni is the atomic density of each element, and σiγ stands for the total microscopic photon atomic cross-section.

The calculation formula of parameter Nelement is defined as follows:

Nelement=mρMififelement× NA×1024    i=Ca,Si,O,Mg,Cl,Fe (3)

where mρ is the mass density of the material being measured, Mi is the atomic weight of each element, fi is the proportion of each element, felement is the proportion of current element, and NA is Avogadro’s constant.

The characteristic gamma rays are not all produced at the bottom of the detection area. They are generated at every location in the detection area, thus, the final correction formula, with a correction factor k, can be rewritten as follows:

I0Ei=IEiexp(μmEiμ0kln(NN0))(1 MeVEi10 MeV) (4)

The main materials in the iron ore concentrate are calcium oxide, silicon dioxide, ferrous oxide, ferric oxide, magnesium oxide, and chlorine. The corresponding composition of each material is listed in Table 3. Iron ore contains six elements: oxygen, magnesium, silicon, calcium, iron, and chlorine; the atomic proportions (fi) of each element are listed in Table 4. The linear absorption coefficient, μ, of iron ore concentrate can be calculated from Eqs. 2 and 4, and the atomic proportions in Table 4. The μmEμ0 data for each element is listed in Table 5.

Table 3
Chemical composition of iron ore, wt(%) relative to dry material
Material   CaO SiO2 TFe FeO MgO Cl
Mass ratio 10.58 5.14 56.33 7.28 2.51 0.25
Show more
TFe=total ferrous content
Table 4
The atomic proportion of the element of iron ore (fi)
Element Ca Si Mg Fe O Cl
 Proportion 0.059933 0.0271758 0.019906 0.3099326 0.5830522 0.002232
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Table 5
μmEμ0 data for each element
Element Cl Hg Ca Si Mg Fe O
Energy (MeV) 6.11 5.967 6.42 3.539 4.934 3.916 7.631 7.646 3.272
μmEμ0 -0.393 -0.395 -0.388 -0.464 -0.415 -0.447 -0.377 -0.377 -0.478
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Using the characteristic energy spectrum, IEi (1 MeV≤Ei≤10 MeV), constant μmEiμ0 (1 MeV≤Ei≤10 MeV), and count rate N and N0 in Equation 4, the energy spectrum after compensation, I0Ei (1 MeV≤Ei≤10 MeV), is obtained.

The gamma-ray self-absorption compensation parameters and data of the six calibration samples are listed in Table 6. The energy spectra before and after gamma-ray self-absorption compensation are shown in Figs. 4a and 4b, respectively. The relationship between the analytical coefficient and iron content, before and after gamma-ray self-absorption compensation, are shown in Figures 5a and 5b, respectively.

Table 6
Gamma self-absorption compensation parameters and data of six calibration samples
Sample 1-1# 1-2# 1-3# 1-4# 1-5# 1-6#
 TFe (wt%) 46.34±0.16 48.23±0.16 50.75±0.16 54.60±0.16 52.85±0.16 58.10±0.16
AFe 6.616 6.799 7.445 7.273 7.996 7.841
N/N0 0.582 0.501 0.528 0.479 0.608 0.452
A1Fe 7.648 8.428 9.063 9.36 9.008 10.594
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AFe means analytic efficient of iron before gamma self-attenuation correction
A1 Fe means analytic efficient of iron after gamma self-attenuation correction
Fig.4
(Color online) Energy spectra of different samples before (a) and after (b) gamma self-absorption compensation
pic
Fig.5.
Relationship between the analytical coefficient and iron content Before (a) and after (b) gamma self-absorption compensation
pic
2.4 Neutron self-absorption correction

Self-absorption in the PGNAA technique is comprised of two parts: gamma-ray self-absorption and neutron self-absorption [16-18]. A bigger neutron-absorption cross-section will result in more neutron self-absorption. The neutron capture reaction cross-section and characteristic gamma-ray energy of different materials are listed in Table 7[19].

Table 7
Neutron capture reaction cross-section of element
Element B O Ca Si Mg Fe Cl
Neutron-absorption cross-section (barns) 764 0.00019 0.431 0.172 0.0666 2.56 33.1
Show more

Previous work regarding neutron self-absorption correction [20] by Professor Wen-bao Jia is compared with the current iron ore concentrate detection experiment in Table 8. It is clear that the total neutron capture cross-section of iron is quite strong in the iron ore concentrate detection experiment, contrasting with the experiment by Professor Jia, which means the influence of sample thickness on detection results is higher than that of previous evaluation.

Table 8
Comparison data of two experiments
Experiment Main element Content (%) Sample weight (kg) TNCCSME(mol∙barns)
Boron solution B 0.3 29 6.148
iron ore concentrate Fe 56.33 110 2.841
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TNCCSME=total neutron capture cross-section of main element

The experimental samples contain silicon, calcium, magnesium, chlorine, and other interfering elements. The test results of iron can be disturbed by these elements. The iron element test result, found by a PGNAA, can be expressed by the following formula:

mFe=KNFeσFenNiσin i=Ca,Si,O,Mg,Cl,Fe (5)

where mFe is the iron grade, as detected by the PGNAA, and K is a constant representing all other contributing factors. σin is the neutron-absorption cross-section of each element listed in Table 7.

The formula for the contribution of each element (excluding iron) to the measurement error of iron is as follows:

(mFe)(Nelement)=KNFeσFeσelementn(Niσin)2=A×σelementn i=Ca,Si,O,Mg,Cl,Fe (6) A=KNFeσFen(Niσin)2    i=Ca,Si,O,Mg,Cl,Fe (7)

The contribution of iron to the measurement error of the iron grade is:

(mFe)(NFe)=K(NiσinNFeσFen)σFen(Niσin)2=A×(NiσinNFeσFenNFe) i=Ca,Si,O,Mg,Cl,Fe (8)

The formula for the total error in iron grade detection is:

ΔmFe=A×0.1856(ΔNCa)2+0.0296(ΔNSi)2+0.0044(ΔNMg)2+0.1166(ΔNFe)2+1095.61(ΔNCl)2 (9)

Formula 9 shows that the changes in the content of chlorine will cause the greatest error in the result. Because chlorine has a large neutron absorption cross-section, the neutron field of the entire system will change considerably when the content of chlorine changes, and, furthermore, it induces more error in the detection of other elements.

The concentration of iron, mFe, and chlorine, mCl, can be expressed as follows [20]:

mFe=(Φ0Φ1)NFeσFenNiσinfηkFe=AFe0kFe   i=Ca,Si,O,Mg,Cl,Fe (10) mCl=(Φ0Φ1)NClσClnNiσinfηkCl=ACl0×kCl   i=Ca,Si,O,Mg,Cl,Fe (11)

where Φ0 and Φ1 are the neutron flux upon it entering (0) and leaving (1) the sample, AFe0 is the analytical coefficient of the energy spectrum of iron when the iron content is mFe, ACl0  is the analytical coefficient of the energy spectrum of chlorine when the content is mCl; kFe and kCl are scaling factors between the concentration and analytic coefficient, f is the geometric factor of the NaI scintillation detector, and η is the detection efficiency.

When the measured sample changes, the iron and chlorine contents become multiples of the original content; p and k, respectively. The corresponding formulas are

mFe=pmFe=(Φ0Φ1)pNFeσFenpNFeσFen+kNClσCln+NOσOn+NSiσSin+NCaσCan+NMgσMgnfηkFe=AFe1kFe (12) mCl=kmCl=(Φ0Φ1)pNClσClnpNFeσFen+kNClσCln+NOσOn+NSiσSin+NCaσCan+NMgσMgnfηkCl=ACl1kCl (13)

where  Φ1' represents the corresponding neutron flux exiting from the surface of the sample, when the iron content of the sample becomes pmFe, the chlorine content of the sample becomes kmCl. AFe1 is the analytical coefficient of the energy spectrum of iron when the iron content is pmFe; ACl1 is the analytical coefficient of the energy spectrum of chlorine when the chlorine content is kmCl; kFe and kCl are scaling factors.

From Equations (10)–(13), the expressions of p and k can be rewritten as:

p=(NOσOn+NSiσSin+NCaσCan+NMgσMgn)(Φ0Φ1')(Φ0Φ1)×AFe0AFe1(Niσin)(AFe0ACl1AFe1ACl0NClσCln+NFeσFen)    i=Ca,Si,O,Mg,Cl,Fe (14) k=(NOσOn+NSiσSin+NCaσCan+NMgσMgn)(Φ0Φ1')(Φ0Φ1)×ACl0ACl1(Niσin)(ACl0AFe1ACl1AFe0NFeσFen+NClσCln)    i=Ca,Si,O,Mg,Cl,Fe (15)

The linear correction factor g(p,k) is defined as:

g(p,k)=(Φ0Φ1)(Φ0Φ1')×pNFeσFen+kNClσCln+NOσOn+NSiσSin+NCaσCan+NMgσMgnNFeσFen+NClσCln+NOσOn+NSiσSin+NCaσCan+NMgσMgn. (16)

To determineφ0, φ1, andφ' 1, a 3He neutron detector was added over the material to detect the neutron flux as shown in Figure 2. Because the measured material itself slows fast neutrons, φ0 is not the thermal neutron flux when the belt is empty. In this experiment, φ0, the thermal neutron flux, was defined when 20 kg carbon powder was placed on the belt.

The final analytical coefficient AFeFinal=AFe1×g(p,k). The data used in the calculation of the calibration samples are listed in Table 9. The calibration data are listed in Table 10. The final total iron calibration curve is shown in Figure 6.

Table 9
Neutron correction parameters and data of the six calibration samples
Sample 1-1# 1-2# 1-3# 1-4# 1-5# 1-6#
A0Fe 9.063 9.063 9.063 9.063 9.063 9.063
A0Cl 0.018 0.018 0.018 0.018 0.018 0.018
A1Fe 7.648 8.428 9.063 9.36 9.008 10.594
A1Cl 0.048 0.038 0.018 0.008 0.026 0.001
p 0.921 0.958 1 1.084 1.044 1.147
k 2.91 2.175 1 0.467 1.517 0.054
φ0-φ1 644.2 644.2 644.2 644.2 644.2 644.2
φ0-φ′1 653.2 670 644.2 629.3 666.7 684.9
g(p,k) 1.091 1.03 1 1.05 1.05 0.981
AFinalFe 8.347 8.684 9.063 9.826 9.459 10.393
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Table 10
Calibration data of the six calibration samples
Sample 1-1# 1-2# 1-3# 1-4# 1-5# 1-6#
Calculate iron content (wt%) 46.41 48.33 50.49 54.83 52.74 58.06
Laboratory iron content (wt%) 46.34 48.23 50.75 54.6 52.85 58.1
Absolute error   (wt%) 0.07 0.1 -0.26 0.23 -0.11 -0.04
RMS error (wt%) 0.16
Show more
RMS=root mean square
Fig. 6.
Iron calibration curve
pic
2.5 Calculation of check samples

To verify the reliability of the method, nine validation samples were prepared. The experimental data of each sample are listed in Table 11. The total iron content comparison curve of the validation samples is shown in Figure 7.

Table 11
Calculation parameters and data of nine check samples
Samples 2-1# 2-2# 2-3# 2-4# 2-5# 2-6# 2-7# 2-8# 2-9#
AFe 6.674 7.054 7.501 7.296 6.977 7.756 7.852 7.698 7.624
N/N0 0.532 0.503 0.556 0.487 0.558 0.591 0.529 0.533 0.451
A0Fe 9.063 9.063 9.063 9.063 9.063 9.063 9.063 9.063 9.063
A0Cl 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018
A1Fe 8.001 8.72 8.702 9.23 8.316 9.051 9.792 9.175 9.942
A1Cl 0.044 0.028 0.033 0.014 0.031 0.022 0.013 0.018 0.005
p 0.925 0.99 1.001 1.045 0.942 1.017 1.08 1.059 1.111
k 2.556 1.601 1.912 0.798 1.761 1.245 0.722 1.046 0.281
φ0-φ1 644.2 644.2 644.2 644.2 644.2 644.2 644.2 644.2 644.2
φ0-φ′1 662.3 639.6 644.2 655.1 670.2 656.3 641.1 650.5 673.5
g(p,k) 1.046 1.029 1.043 1.027 1.023 1.019 1 1.046 1.012
AFe 8.39 8.972 9.074 9.475 8.566 9.219 9.789 9.6 10.066
Calculate iron content (wt%) 47.21 50.32 50.86 53.01 48.15 51.64 54.69 53.67 56.16
Laboratory iron content (wt%) 47.29 49.49 50.54 52.68 48.55 51.8 55.48 53.73 56.35
Absolute error (wt%) -0.08 0.83 0.32 0.33 -0.4 -0.16 -0.79 -0.06 -0.19
RMS error (wt%) 0.45
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Fig. 7.
Check samples comparison curve
pic

3 Results and Discussion

The experiment adopts the spectrum library least-squares approach to analyze the spectrum, effectively eliminating the influence of interference elements. The spectrum library was established before the experiment and contains the characteristic energy spectra of calcium, silicon, iron, aluminum, magnesium, chlorine, sulfur, sodium, and the background. Through the least-squares operation, the contribution of each element in the total spectrum can be found, which corresponds to the content of the element.

Because of the strong gamma-ray self-absorption and neutron-absorption effect of iron, the PGNAA detection result is quite poor, and thus, both gamma-ray self-absorption correction and neutron self-absorption correction should be incorporated into PGNAA detection.

Figure 4b shows the compensation effect of energy spectra at different iron concentrations. Figure 5a and 5b gives the relationship between the analytical coefficient and the iron content before and after gamma-ray self-absorption correction, respectively. Before compensation, the linear correlation coefficient between the analytical coefficient and the iron content is 0.79747 and is improved to 0.96627 after energy spectrum compensation.

Owing to the large neutron caption cross-section of iron and chlorine, which considerably disturb the iron grade detection result, the experimental results should be corrected to eliminate the interference of chlorine. As seen in Figure 6, after neutron self-absorption correction and chlorine interference correction, the linear correlation coefficient between iron content and the analytical coefficient reaches 0.99886.

Figure 7 shows the total iron content comparison curve of the validation samples, in which the trend of calculated value is consistent with the actual value. The RMS error of the validation samples is 0.45, which is the ideal result.

4 Conclusion

Based on the PGNAA technique and a new correction algorithm, the linear correlation coefficient between the total iron content and analytical coefficient of six calibration samples was improved to 0.99886, and the RMS error of nine validation samples was decreased to 0.45, which is the ideal result. The PGNAA technique can be applied to real-time heavy element concentrate detection.

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