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.
-201904/1001-8042-30-04-006/alternativeImage/1001-8042-30-04-006-F001.jpg)
-201904/1001-8042-30-04-006/alternativeImage/1001-8042-30-04-006-F002.jpg)
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.
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 |
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 |
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.
-201904/1001-8042-30-04-006/alternativeImage/1001-8042-30-04-006-F003.jpg)
2.3 Gamma-ray self-absorption correction
The following compensation formula [22] for gamma-ray self-absorption is used to correct for self-attenuation:
where
The linear absorption coefficient,
where Ni is the atomic density of each element, and
The calculation formula of parameter Nelement is defined as follows:
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,
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:
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
Material | CaO | SiO2 | TFe | FeO | MgO | Cl |
---|---|---|---|---|---|---|
Mass ratio | 10.58 | 5.14 | 56.33 | 7.28 | 2.51 | 0.25 |
Element | Ca | Si | Mg | Fe | O | Cl |
---|---|---|---|---|---|---|
Proportion | 0.059933 | 0.0271758 | 0.019906 | 0.3099326 | 0.5830522 | 0.002232 |
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 |
-0.393 | -0.395 | -0.388 | -0.464 | -0.415 | -0.447 | -0.377 | -0.377 | -0.478 |
Using the characteristic energy spectrum,
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.
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 |
-201904/1001-8042-30-04-006/alternativeImage/1001-8042-30-04-006-F004.jpg)
-201904/1001-8042-30-04-006/alternativeImage/1001-8042-30-04-006-F005.jpg)
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].
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 |
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.
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 |
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:
where
The formula for the contribution of each element (excluding iron) to the measurement error of iron is as follows:
The contribution of iron to the measurement error of the iron grade is:
The formula for the total error in iron grade detection is:
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,
where
When the measured sample changes, the iron and chlorine contents become multiples of the original content;
where
From Equations (10)–(13), the expressions of p and k can be rewritten as:
The linear correction factor
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
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 |
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 |
-201904/1001-8042-30-04-006/alternativeImage/1001-8042-30-04-006-F006.jpg)
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.
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 |
-201904/1001-8042-30-04-006/alternativeImage/1001-8042-30-04-006-F007.jpg)
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.
Detection sensitivities of C and O in coal due to a channel in the noderator
. Radiat Meas. 46, 88-91 (2011). Doi: 10.1016/j.radmeas.2010.08.025A Monte Carlo comparison of PGNAA system performance using 252Cf neutrons, 2.8-MeV neutrons and 14-MeV neutrons
. Nucl. Instrum. Meth. A 511, 400-407 (2003). Doi: 10.1016/s0168-9002(03)01949-1Investigation of PGNAA using the LaBr3 scintillation detector
. Appl. Radiat. Isot. 68, 901-904 (2010). Doi: 10.1016/j.apradiso.2009.09.058Density and water content corrections in the gamma count rate of a PGNAA system for cement raw material analysis using the MCNP Code
. Appl. Radiat. Isot. 49, 923-930 (1998). Doi: 10.1016/s0969-8043(97)10111-7Moderator-collimator-shielding design for neutron radiography systems using 252Cf
. Appl. Radiat. Isot. 54, 217-225 (2001). Doi: 10.1016/s0969-8043(00)00291-8A Mente Carlo study of the influence of the geometry arrangements and structural materials on a PGNAA system performance for cement raw material analysis
. Appl. Radiat. Isot. 48, 1349-1354 (1997). Doi: 10.1016/s0969-8043(97)00130-9Mc simulation of a PGNAA system for on-line cement analysis
. Nucl. Sci. Tech. 21, 221-226 (2010). Doi: 10.13538/j.1001-8042/nst.21.221-226Performance comparison of an 241Am-be neutron source-based pgnaa setup with the kfupm pgnaa setup
. J. Radioanal. Nucl. Chem. 260, 641-646 (2004). Doi: 10.1023/b :jrnc.0000028225.07280.74Monte Carlo simulation of PGNAAsystem for determining element content in the rock sample
. J. Radioanal. Nucl. Chem. 299, 1219-1224 (2014). Doi: 10.1007/s10967-013-2858-3Status and Development of prompt γ-ray neutron activation analysis
. Atomic Energy Science and Technology. 39, 282-288 (2005). Doi: 10.3969/j.issn.1000-6931.2005.03.022 (in Chinese)Neutron activation analyzer radiological monitoring system
. Modern Mining. 8, 188-189 (2017). Doi: 10.3969/j.issn.1674-6082.2017.08.059An on-belt elemental analyser for the cement industry
. Appl. Radiat. Isot. 54, 11-19 (2001). Doi: 10.1016/S0969-8043(00)00180-9Feasibility study for on-line analysis of bauxite using a PGNAA system
. China Mining Magazine. 10, 171-174 (2015). Doi: 10.3969/j.issn.1004-4051.2015.10.037 (in Chinese)Identification system for chemical warfare agents with PGNAA method
. Nuclear Electronics and Detection Technology. 27, 621-623 (2007). Doi: 10.3969/j.issn.0258-0934.2007.04.002 (in Chinese)Adjustable multi element analyzer
, 2008Study of influence of neutron field and γ-ray self-absorption on PGNAA measurement
. Atomic Energy Science and Technology. 48, 802-806 (2014). Doi: 10.7538/yzk.2014.48.S0.0802 (in Chinese)Gamma-ray attenuation coefficients of some building materials available in Egypt
. Ann. Nucl. Energy. 36, 849-852 (2009). Doi: 10.1016/j.anucene.2009.02.006Research on accurate calculation method of γ-ray self-absorption correction factor
. Atomic Energy Science and Technology. 51, 323-329 (2017). Doi: 10.7538/yzk.2017.51.02.0323 (in Chinese)At. Data Nucl. Data Tables 80, 1
, 2002. https://www-nds.iaea.org/pgaaStudy on the elements detection and its correction in aqueous solution
. Nucl. Instrum. Meth. B. 342, 240-243 (2015). Doi: 10.1016/j.nimb.2014.10.010A simple method for correcting the neutron self-shielding effect of matrix and improving the analytical response in prompt gamma-ray neutron activation analysis
. Analytica. Chimica. Acta. 549, 205-211 (2005). Doi: 10.1016/j.aca.2005.06.021