A Nonlinear Integrated Modeling Method of Extended Kalman Filter Based on Adaboost Algorithm

Abstract In the zinc hydrometallurgical purification process, the concentration ratio of zinc ion to trace nickel ion is as high as 10⁵, so that the nickel spectral signal is completely covered by high concentration zinc signal, resulting in low sensitivity and nonlinear characteristics of nickel spectral signal. Aiming at the problem that it is difficult to detect nickel in zinc sulfate solution, this paper proposes a nonlinear integrated modeling method of extended Kalman filter based on Adaboost algorithm. First, a non-linear nickel model is established based on nickel standard solution. Second, an extended Kalman filter wavelength optimization method based on correlation coefficient is proposed to select wavelength variables with high signal sensitivity, large amount of information and strong nonlinear correlation. Finally, a nonlinear integrated modeling method based on Adaboost algorithm is proposed, which uses extended Kalman filter as a basic submodel, and realizes the stable detection of trace nickel through the weighted combination of multiple basic models. The results show that the average relative error of this method for detecting nickel is 4.56%, which achieves accurate detection of trace nickel in zinc sulfate solution.

Introduction

Zinc (Zn) is the third largest non-ferrous metal after aluminum and copper (Yadav and Banerjee, 2018). At present, 80% of zinc in the world is produced by zinc hydrometallurgy (Zhou et al., 2019), which mainly includes grinding, leaching, purification and electrolysis processes (Zhang et al., 2018; Li et al., 2018). Among them, the purification process is a key process of zinc hydrometallurgy (Luo et al., 2019), through the accurate detection of impurity ion concentration in the electrolyte, and then based on the zinc powder replacement method to remove impurity ions, that is the premise to ensure the normal operation of zinc hydrometallurgy (Zahmatkesh, et al., 2017; Molognoni et al., 2018). However, manual offline analysis of the impurity ion concentration is still used in the current production (Kočanová et al., 2017). The detection is time-consuming (Chen et al., 2018), the process is cumbersome (Chen et al., 2017), and the feedback information is lagging (Dong et al., 2018), so it is impossible to optimize and adjust the process parameters of the zinc hydrometallurgical purification process in real time (He et al., 2016). Usually, excessive addition of zinc powder is used to ensure the impurity removal effect, resulting in large consumption of zinc powder (Li et al., 2017), large fluctuation of impurity ion concentration (Walash et al., 2009), low production efficiency and unqualified product quality (Zhou et al., 2009; Ji et al., 2012), which restrict the high-efficiency and green production of purification process (Liu et al., 2017). Therefore, it is urgent to realize the on-line detection of the concentration of impurity metal ions in zinc hydrometallurgy.

In recent years, the commonly used methods for on-line detection of metal ions include potentiometric titration (Attimarad 2012), polarography (Duran Meras et al., 2002), inductively coupled plasma mass spectrometry (Rastogi et al., 2015), ultraviolet visible spectroscopy (Lambert et al., 2017) and laser-induced breakdown spectroscopy (Fedenko et al., 2017). As a conventional quantitative analysis method, ultraviolet visible spectroscopy is widely used in the field of analysis and detection due to its advantages of simplicity, accuracy, rapidity, multi-function and low cost (Lepane et al., 2015; Lee and Oh, 2017). However, in the zinc hydrometallurgical purification process, when using ultraviolet-visible spectroscopy to detect nickel (Ni) in zinc sulfate solution, there are the following difficulties (Rote and Bari, 2009; Khan et al., 2020): 1) in zinc sulfate solution, the concentration ratio of main zinc to nickel ion is as high as 10⁵, which makes the nickel spectral signal seriously masked by the main zinc signal; 2) the chemical characteristics of zinc and nickel in zinc solution are similar, and the spectral characteristic information area is concentrated and the effective band is narrow, which makes their spectral signal seriously overlap and interfere with each other; 3) due to the increase of particle density in zinc sulfate solution, the absorptivity and transmissivity of the solution to the incident light are changed, resulting in the spectral characteristics of nickel in the solution seriously deviate from Beer-Lambert law, which makes it difficult to quantitatively analyze and detect nickel; 4) due to the fluctuation of the main zinc, the random noise of the testing instrument and the weak background interference of reagents such as chromogenic agents, these factors will affect the detection accuracy of nickel ion. The above-mentioned problems have brought great challenges to detecting the concentration of nickel ion in zinc sulfate solution based on ultraviolet-visible spectroscopy.

In order to solve the problem that it is difficult to detect the concentration of nickel ion in zinc sulfate solution, this paper proposes a nonlinear integrated modeling method of extended Kalman filter based on Adaboost algorithm. First, a non-linear nickel model is established based on nickel standard solution. Second, an extended Kalman filter wavelength optimization method based on correlation coefficient is proposed to select wavelength variables with high signal sensitivity, large amount of information and strong nonlinear correlation. Finally, a nonlinear integrated modeling method based on Adaboost algorithm is proposed, which uses extended Kalman filter as a basic submodel, and realizes the stable detection of trace nickel ion through the weighted combination of multiple basic models. The results show that the average relative error of this method for detecting nickel ion is 4.56%, which achieves accurate detection of trace nickel ion in high concentration zinc solution.

Theory

A. Extended Kalman Filter

Kalman filter spectrophotometry takes the minimum mean square error as the criterion to mathematically process a series of measurement data containing errors (Ben-Ari and Ben-shahar, 2013). It is suitable for the spectrophotometric analysis of multi-component systems and is currently mainly used for multi-component linear modeling (Ji et al., 2012). Aiming at the nonlinearity of nickel in high-concentration zinc solution, based on the Kalman filter spectrophotometry, this paper proposes an extended Kalman filter spectrophotometric method based on ultraviolet-visible spectroscopy to detect nickel ion in high concentration zinc solution. Generally, the extended Kalman filter (EKF) describe a nonlinear system using a system model and a measurement model, these two models can be expressed as follows:

$X\left(k\right)=X\left(k-1\right)+W\left(k\right)(1)$

$Z\left(k\right)=h\left[X\left(k\right)\right]+V\left(k\right)(2)$

where, $k$ represents the wavelength, $X\left(k\right)$ is the concentration, $W\left(k\right)$ is the system noise, $h[·]$ represents the non-linear absorption coefficient related to the concentration $X\left(k\right)$, $Z\left(k\right)$ represents the absorbance and $V\left(k\right)$ represents the measurement noise.

By expanding Eq. 2 according to the Taylor series and omitting the terms of the second order and above, it is obtained that:

$Z\left(k\right)=h\left[\stackrel{\wedge }{X}\left(k|k-1\right),k\right]+{\frac{\partial h}{\partial \stackrel{\wedge }{X}\left(k\right)}|}_{\stackrel{\wedge }{X}\left(k|k-1\right)}\left[X\left(k\right)-\stackrel{\wedge }{X}\left(k|k-1\right)\right]+V\left(k\right)(3)$

and set as

$H\left(k\right)={\frac{\partial h}{\partial \stackrel{\wedge }{X}\left(k\right)}|}_{\stackrel{\wedge }{X}\left(k|k-1\right)}y\left(k\right)=h\left[\stackrel{\wedge }{X}\left(k|k-1\right),k\right]-{\frac{\partial h}{\partial \stackrel{\wedge }{X}\left(k\right)}|}_{\stackrel{\wedge }{X}\left(k|k-1\right)}\stackrel{\wedge }{X}\left(k|k-1\right)(4)$

From Eq. 3 and Eq. (4), the measurement model can be written as follows:

$Z\left(k\right)=H\left(k\right)X\left(k\right)+y\left(k\right)+V\left(k\right)(5)$

According to the linearization models of Eq. 1 and Eq. (5), the optimal estimate can be obtained from the previous estimate and the current measurement, and is given by:

$\stackrel{\wedge }{X}\left(k\right)=\stackrel{\wedge }{X}\left(k-1\right)+K\left(\text{k}\right)\left[\text{Z}\left(k\right)-H^T\left(k\right)\cdot X\left(k-1\right)\right](6)$

In Eq. 6, $K\left(k\right)$ represents the Kalman gain matrix, given by

$K\left(k\right)=P\left(k-1\right)H\left(k\right){\left[H^T\left(k\right)P(k-1)H\left(k\right)+R\left(k\right)\right]}^{-1}(7)$

where, $R\left(k\right)$ is the measurement noise of the instrument and $P\left(k-1\right)$ is the error covariance matrix, respectively expressed as follows:

$R\left(k\right)=\frac{1}{m}{\displaystyle \sum _{k=1}^{m}V\left(k-1\right)}V\left(k-1\right)-H^T\left(k\right)P\left(k-1\right)H\left(k\right)(8)$

$P\left(k\right)=\left[I-K\left(k\right)H^T\left(k\right)\right]P\left(k-1\right){\left[I-K\left(k\right)H^T\left(k\right)\right]}^T+K\left(k\right)R\left(k\right)K^T\left(k\right)(9)$

Eq. 1, Eq. 2, Eq. 3, Eq. 4, Eq. 5, Eq. 6, Eq. 7, Eq. 8, and Eq. 9 constitute the basic extended Kalman filter spectrophotometry.

B. Integrated Modeling Based on Adaboost Algorithm

In zinc sulfate solution, the concentration ratio of zinc ion to nickel ion is as high as 10⁵, which leads to low sensitivity and strong nonlinearity of nickel spectral signal. The extended Kalman filter algorithm proposed above can better detect nickel concentration in zinc solution, but the relative error varies greatly. The main reasons for this problem are the fluctuation of the main zinc, the mutual interference and suppression between multi metal ions, the random noise of detection instrument and the weak background interference of reagents such as chromogenic reagent. These factors will affect nickel absorbance, thus affecting the detection accuracy and repeatability of a single sample, resulting in excessive sample difference.

Integrated modeling is an effective method to solve the low stability of a single model. Its core idea is to form multiple training sets from a same training set randomly or in combination, then build sub-models based on these training sets, and use the sub-models to predict separately, and finally use the integrated method to form a final result. In this paper, the idea of integrated modeling is applied to the concentration detection of trace nickel in high-concentration zinc solution, and an integrated modeling method based on Adaboost algorithm is proposed. Taking extended Kalman filter as the basic sub-model, through the weighted combination of multiple basic models, the weight of weak classifiers with a large classification error rate is reduced, while the weight of weak classifiers with a small classification error rate is increased, so as to improve the sample detection accuracy, enhance the stability of the model, and realize the stable detection of trace nickel in zinc sulfate solution. The flow chart of Adaboost training sample is shown in Figure 1.

FIGURE 1

FIGURE 1. The flow chart of Adaboost training sample.

In the Adaboost algorithm, the weight distribution of training samples is initialized firstly. Assuming that there are a total of N training samples, each sample is assigned the same sample weight value 1/N, and these weight values constitute the vector D. The specific implementation steps are as follows:

1) Initialize the weight distribution of training samples:

$D_l=\left\{w_{ll},\cdot \cdot \cdot w_{li},\cdot \cdot \cdot ,w_{lN}\right\},w_{li}=1/N,i=\mathrm{1,2},\cdot \cdot \cdot ,N(10)$

2) These samples are used to train the weak classifier, and the weight of samples is adjusted to train iteratively. m is the mth iteration, and the maximum number of iterations $M_r$ is set to 40.

3) According to the characteristic wavelength variables, several weak models of EKF are randomly generated. The weak model with the lowest error rate is selected as the mth basic model to predict the validation samples, and the maximum error rate and the relative error of each sample are calculated.

$E_m=\max \left|y_i-G_m\left(x_i\right)\right|(11)$

${\epsilon }_{mi}=\frac{\left|y_i-G_m\left(x_i\right)\right|}{E_m}(12)$

4) The total error rate of the mth basic model is calculated.

${\epsilon }_m={\displaystyle \sum _{i=1}^N{w}_{mi}}{\epsilon }_{mi}(13)$

5) The weight of the mth weak classifier H_m(x) in the final model is calculated.

${\alpha }_m=\frac{1}{2}\ln \left(\frac{1-{\epsilon }_m}{{\epsilon }_m}\right)sign\left(\frac{1}{2}\ln \left(\frac{1-{\epsilon }_m}{{\epsilon }_m}\right)\right)(14)$

According to Eq. 14, ${\alpha }_m$increases with the decrease of ${\epsilon }_m$, which indicates that in the final classifier, the weight proportion of weak classifier with small classification error rate can be increased.

6) Updating the weight distribution of training set.

$D_{m+1}=\left\{w_{m+1,l},\cdot \cdot \cdot w_{m+1,i},\cdot \cdot \cdot ,w_{m+1,N}\right\},i=\mathrm{1,2},\cdot \cdot \cdot ,N(15)$

$w_{m+1,i}=\frac{w_{mi}\exp \left(-{\alpha }_m{y}_i\widehat{y_i}\right)}{Z_m}(16)$

$Z_m=2\sqrt{{\epsilon }_m\left(1-{\epsilon }_m\right)}(17)$

where, $y_i$ and $\widehat{y_i}$ represent the calibration value and predicted value of the ith sample respectively, and $Z_m$ represents the normalization factor.

7) If the number of iterations exceeds the set threshold, the trained weak classifiers are combined into strong classifiers.

$f\left(x\right)=sign\left({\displaystyle \sum _{k=1}^K{\alpha }_{k}G\left(x\right)}\right)(18)$

Experimental

A. Reagents

All chemicals were analytical reagents and no further purification was required. Deionized water was used as solvent to prepare 50 g/L zinc and 12.5 mg/L nickel stock solutions. The standard solution was then prepared by continuous dilution of the stock solution as required. Acetic acid-sodium acetate buffer (pH = 5.5) was prepared by mixing an appropriate volume of pure acetic acid and sodium acetate. Ethylene Diamine Tetraacetic Acid (EDTA, 1.0 mol/L) was used as a masking solution to reduce the absorbance of zinc. Cetyltrimethylammonium bromide (CTAB, 0.01 mol/L) was used as a stabilizer solution. Nitroso-R salt solution (0.4%) was prepared as a chromogenic reagent.

B. Apparatus

An Optosky ATP2000 micro spectrometer (Optosky Technology Ltd., China) was used to measure the absorbance spectra. Quartz cuvettes (1 cm) were matched and used for all absorbance measurements. ATP2000 is a high-sensitivity miniature optical fiber spectrometer. It adopts a 2048 × 64 pixel refrigerated linear back-illuminated CCD detector, which greatly reduces the noise of the sensor and improves the reliability of measurement. The detection spectral wavelength range is 180–1100 nm, the optical resolution is up to 0.1 nm, and the measured spectral data is output through USB2.0 or UART port.

C. Procedures

In a 25 ml calibration flask, add different proportions of zinc and nickel standard solutions, 7.5 ml acetic acid-sodium acetate buffer solution (pH = 5.5) and 5.00 ml Nitroso R salt solution, and dilute to the calibration scale with an appropriate volume of distilled water. The blank solution was prepared in the same way. The final concentration range of zinc is 20–30 g/L, and that of nickel is 0.6–6.0 mg/L. The ATP-2000 spectrophotometer is used to measure the spectral signal of the mixed solution, scanning in the wavelength range of 350–800 nm at 1 nm interval. All measured spectra are the average of five repeated measurements.

Results and Discussion

A. Spectral Characteristics

The basic principle of ultraviolet-visible absorption spectroscopy detection is Beer-Lambert law, that is, when a beam of parallel monochromatic light passes through a uniform colored solution, when the optical path is fixed, the absorbance of the solution is proportional to the concentration of the solution. Figure 2A shows the absorption spectral signal of a 0.6 mg/L nickel solution. There are characteristic peaks at wavelengths of 302 and 455 nm, and the maximum absorbance is 0.51. Figure 2B shows the spectral signal of a 20 g/L zinc solution, with a characteristic peak at a wavelength of 441 nm, and a maximum absorbance of 4.149. Figure 2C shows the spectral signal of nickel (0.6 mg/L), zinc (20 g/L) and their mixture in 250–600 nm. It can be seen from Figure 2C that the absorbance of zinc is close to the absorbance of its mixture, which almost completely masks the nickel signal, resulting in a lower absorbance of nickel. From the partial enlarged view of nickel signal, it can be seen that the characteristic peak of nickel is shifted due to the influence of high concentration zinc signal, and the characteristic peak appears at the wavelength of 486 nm, and the maximum absorbance is only 0.15. In 250–300 nm, due to the supersaturation of zinc ion, the measured absorbance exceeds the maximum range of the instrument, and the measured value is not available. In addition, because zinc and nickel have similar chemical properties, the absorption spectra of zinc and nickel are seriously overlapped in the entire wavelength range. Therefore, it is difficult to detect the concentration of nickel in high concentration zinc solution.

FIGURE 2

FIGURE 2. Absorption spectra of zinc and nickel. (A) Absorption spectra of pure nickel solution; (B) Absorption spectra of pure zinc solution: Show results in wavelength range from 375 nm to 600 nm and Absorbance range from 0 to 6 (never below 0); (C) Absorption spectra of zinc, nickel and their mixtures: Show results in wavelength range from 300 nm to 600 nm and Absorbance range from 0 to 6 (never below 0); Show results in wavelength range from 475 nm to 600 nm and Absorbance range from 0 to 0.2 (never below 0).

The absorption spectra of zinc (20–30 g/L) are shown in Figure 3, it can be seen that as the zinc concentration increases, there is almost no change in absorbance. The reason is that the concentration of zinc is oversaturated, which leads to the relationship between its absorbance and concentration no longer obeys Beer-Lambert law. Therefore, in the detection of nickel concentration in zinc sulfate solution, the preparation of 20 g/L zinc solution as a reference solution can eliminate the interference of zinc on nickel signal in their mixed solution, and improve the sensitivity and resolution of nickel spectral signal.

FIGURE 3

FIGURE 3. The absorption spectral signal of zinc solution in the range of 20–30 g/L: Show results in wavelength range from 390 nm to 600 nm and Absorbance range from 0 to 6 (never below 0).

B. Univariate Calibration

In order to evaluate the linearity of trace nickel in zinc sulfate solution, 20 groups of 0.6–6.0 mg/L nickel standard solution and a 20 g/L zinc solution as reference were prepared. The calibration curve was constructed by using the absorbance of nickel at the maximum peak (wavelength 486 nm) and the corresponding concentration. The linear and nonlinear models were used for calibration respectively. The nickel spectral signal and calibration curve are shown in Figure 4.

FIGURE 4

FIGURE 4. Calibration curve for nickel. (A) Absorption spectra of nickel standard solutions with different concentrations: Show results in wavelength range from 475 nm to 600 nm and Absorbance range from 0 to 6 (never below 0). (B) Linear calibration curve. (C) Nonlinear calibration curve.

Figure 4A shows the absorption spectra of 20 groups standard solutions of nickel ion at different concentrations with 20 g/L zinc as reference. Figure 4B shows the linear correction of nickel at 486 nm. It can be seen that the linear correction curve has a large deviation from the actual measured value, indicating that the nickel linearity is very poor. Figure 4C shows the non-linear calibration curve of nickel at 486 nm, which is fitted by the fourth-order polynomial. It can be seen that the fitting effect is good, indicating that the non-linear calibration curve can well reflect the spectral characteristics of nickel, in which the regression coefficient is 0.9963, and the fitting coefficient is (0.0037, −0.0448, 0.1760, −0.2303, 0.2054).

C. Extended Kalman Filter Spectrophotometry

According to nickel spectral characteristics, in the whole wavelength range, the nickel spectral signal completely overlaps with zinc, and the nickel spectra exhibits nonlinearity. When the zinc concentration is oversaturated, its absorbance remains unchanged. The interference of zinc can be eliminated by the difference of spectral signal between the measuring solution and the 20 g/L zinc solution, and then the nickel concentration can be detected iteratively by extended Kalman filter spectrophotometry. In order to improve the accuracy of the EKF model and reduce the calculation time, this paper uses the wavelength selection method based on correlation coefficient to select wavelength variables. The RCE value represents the ratio of correlation coefficient to estimation error, which helps accelerate the convergence speed of filtering and improve the accuracy of the EKF model, shown in Figure 5. It can be seen that the RCE value changes drastically and only stabilizes in the wavelength range of 410–540 nm, which shows that in this wavelength range, the nickel spectral signal has high sensitivity, large amount of information and high correlation coefficient.

FIGURE 5

FIGURE 5. The RCE value of nickel at different wavelengths.

In order to evaluate the performance of extended Kalman filter (EKF), 10 groups of nickel and zinc mixed solutions with different concentrations were prepared. The concentration of zinc is 20–30 g/L and that of nickel is 0.6–6 mg/L. During the measurement, a 20 g/L zinc solution is prepared as the reference solution. The extended Kalman filter spectrophotometry (EKF) was used to detect nickel in 10 groups of mixed solutions. The predicted and calibrated values of nickel ion are shown in Figure 6. The maximum prediction relative error of nickel concentration is 16.14%, and the average relative error is 7.28%. The root mean square error of prediction (RMSEP) is 0.2739. The results show that the extended Kalman nonlinear modeling method can be used for the real-time detection of nickel ion in zinc solution, but the detection accuracy needs to be further improved.

FIGURE 6

FIGURE 6. Predicted and actual concentration values of nickel in mixture solution.

D. Integrated Modeling Based on Adaboost Algorithm

The proposed extended Kalman filter algorithm can detect nickel in zinc sulfate solution, but the relative error varies greatly, and individual sample error even exceed 10%, which can not meet the requirements of industrial detection. The main reasons for this problem are the fluctuation of the matrix zinc, the mutual interference and suppression between multi metal ions, the random noise of measuring instrument and the weak background interference of reagents such as chromogenic agent. In view of the instability of the extended Kalman algorithm model due to the above reasons, it is necessary to make full use of the characteristic wavelength (410–540 nm) of a single sample to minimize the impact of individual wavelength. In this paper, the idea of integrated modeling is applied to the concentration detection of trace nickel in high concentration zinc solution. The integrated modeling based on the Adaboost algorithm takes the extended Kalman filter as the basic sub model. Through the weighted combination of several basic models, the weight of the weak classifier with large classification error rate is reduced, while the weight of the weak classifier with small classification error rate is increased, so as to improve the sample detection accuracy, enhance the stability of the model, and realize the stable detection of trace nickel in high concentration zinc solution.

The more important factor in integrated modeling is the number of weak models. When the number of weak models is too small, the random combination cannot fully cover all the characteristic wavelength information, which affects the accuracy of the results. If the number of weak models is too large, the computational complexity will be increased and the real-time performance of detection will be affected. Figure 7 shows the estimated error graphs using different models. It can be seen from Figure 7 that with the increase of the number of weak models, the estimation error of the model gradually decreases. When the number of weak models is 60, the model gradually tends to be stable, and then increase the number of weak models, the estimation error is basically unchanged. Therefore, the number of weak models is set to 60.

FIGURE 7

FIGURE 7. The relationship between the estimation error and the number of weak models.

E. Determination of Nickel by EKF_Adaboost Method

In order to evaluate the performance of the EKF_Adaboost method, ten sets of mixed solutions containing different proportions of Zn and Ni were prepared, and a 20 g/L zinc solution was prepared as a reference. The predicted concentrations of Ni are shown in Table 1. It can be seen that the maximum prediction relative error of nickel is 7.13%, the average relative error is 4.39%, and the root mean square error of prediction (RMSEP) is 0.165. In order to further verify the stability of the EKF_ Adaboost method, 30 repeatability tests were performed on the nickel experimental data, and the PLS, EKF and EKF_Adaboost models were used to detect nickel concentration. The performance comparison results are shown in Table 2.

TABLE 1

TABLE 1. The predicted concentrations of Ni by EKF_Adaboost method.

TABLE 2

TABLE 2. Comparison of PLS, EKF and EKF_ Adaboost models.

It can be seen from Table 2 that due to the strong nonlinearity between the absorbance and concentration of nickel ion, the performance of using the PLS method to detect nickel concentration is very poor. The maximum relative error is 76.57%, the average relative error is 28.93%, and the detection accuracy is only 71.07%, which can not to meet the requirements of industrial detection. The EKF method uses nonlinear modeling, the average relative error is 9.38%, the detection accuracy is 90.62%, which can better meet the requirements of industrial detection. However, EKF model relies on wavelength variables. When the sample changes due to the random fluctuation of matrix zinc, mutual interference between multi metal ions and random noise of testing instrument, the performance of some wavelength variables of EKF model becomes worse, which will seriously affect the prediction accuracy of nickel ion. EKF_AdaBoost adopts the idea of integrated modeling, which can reduce the dependence on wavelength. The average relative error is 4.56%, and the detection accuracy is 95.44%. Therefore, the EKF_AdaBoost method can realize the real-time detection of impurity nickel ion in zinc sulfate solution.

Conclusions

In the zinc hydrometallurgical purification process, the concentration ratio of zinc ion to trace nickel ion is as high as 10⁵, and the spectral signal of zinc and nickel overlap seriously, which makes the nickel signal completely masked by the high concentration zinc signal, resulting in the low sensitivity and nonlinear characteristics of the nickel spectral signal. Aiming at the problem that it is difficult to detect nickel in high zinc solution, an extended Kalman nonlinear integrated modeling method based on Adaboost is proposed in this paper to realize the accurate detection of nickel in zinc sulfate solution. The PLS, EKF, and EKF_Adaboost models are used to analyze and detect nickel concentration, and the performance of different models is compared. The results show that EKF_Adaboost adopts the idea of integrated modeling, which can reduce the dependence on wavelength, with an average relative error of 4.56% and a detection accuracy of 95.44%. Therefore, the EKF_Adaboost method can realize real-time detection of impurity nickel concentration in zinc hydrometallurgical purification process, and will be applied to other spectral signals such as infrared spectra, Raman spectra, and more.

Data Availability Statement

The original contributions presented in the study are included in the article/Supplementary Material, further inquiries can be directed to the corresponding authors.

Author Contributions

F-BZ conducted experiments and drafted the original manuscript. Research conception was initiated by H-QZ along with gaining funding, writing, reviewing, and editing. C-GL and H-QZ contributed to writing and reviewing. All authors contributed to the article and approved the submitted version.

Funding

This work was supported in part by the key Project for International Cooperation and Exchange of the National Natural Science Foundation of Chinaunder Grant No. 61860206014, and in part by Research Foundation of Hunan Provincial Education Department under Grant No. 19B518.

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

References

Attimarad, M. (2012). Simultaneous Determination of Ofloxacin and Flavoxate Hydrochloride by First-And Ratio First-Derivative UV Spectrophotometry. J. Iran Chem. Soc. 9, 551–557. doi:10.1007/s13738-012-0068-5

CrossRef Full Text | Google Scholar

Ben-Ari, R., and Ben-Shahar, O. (2013). A Computationally Efficient Tracker with Direct Appearance-Kinematic Measure and Adaptive Kalman Filter. J. Real-time Image Proc. 11, 271–285. doi:10.1007/s11554-013-0329-2

CrossRef Full Text | Google Scholar

Chen, Y.-f., Zhi-xiong, Li., Zhen-wei, Z., Qing-lin, X., Yao-zhuang, N., and Guang-hua, G. (2018). Nonlinear Gyrotropic Motion of Skyrmion in a Magnetic Nanodisk. J. Magnetism Magn. Mater. 458, 123–128. doi:10.1016/j.jmmm.2018.03.016,

CrossRef Full Text | Google Scholar

Chen, Z., Li, H., He, Z., Xu, H., Zheng, M., and Zhao, M. (2017). Multiple Plasmon-Induced Transparency Effects in a Multimode-Cavity-Coupled Metal-Dielectric-Metal Waveguide. Appl. Phys. Express 10, 092201. doi:10.7567/apex.10.092201

CrossRef Full Text | Google Scholar

Dong, L., Xu, X., Li, C., Guo, Y., Sun, K., and Ding, Y. (2018). Plasmon-induced Transparency in Sensing Application with Semicircle Cavity Waveguide. Opt. Commun. 410, 751–755. doi:10.1016/j.optcom.2017.11.048

CrossRef Full Text | Google Scholar

Durán Merás, I., Espinosa Mansilla, A., Salinas López, F., and Rodríguez Gómez, M. (2002). Comparison of UV Derivative-Spectrophotometry and Partial Least-Squares (PLS-1) Calibration for Determination of Methotrexate and Leucovorin in Biological Fluids. Anal. Bioanal. Chem. 373, 251–258. doi:10.1007/s00216-002-1348-1

PubMed Abstract | CrossRef Full Text | Google Scholar

Fedenko, V. S., Shemet, S. A., and Landi, M. (2017). UV-vis Spectroscopy and Colorimetric Models for Detecting Anthocyanin-Metal Complexes in Plants: An Overview of In Vitro and In Vivo Techniques. J. Plant Physiol. 212, 13–28. doi:10.1016/j.jplph.2017.02.001

CrossRef Full Text | Google Scholar

He, Z., Li, H., Li, B., Chen, Z., Xu, H., and Zheng, M. (2016). Theoretical Analysis of Ultrahigh Figure of merit Sensing in Plasmonic Waveguides with a Multimode Stub. Opt. Lett. 41, 5206–5209. doi:10.1364/OL.41.005206

PubMed Abstract | CrossRef Full Text | Google Scholar

Ji, H., Xu, Y., Li, S., Xin, H., and Cao, H. (2012). Simultaneous Determination of Iron and Manganese in Water Using Artificial Neural Network Catalytic Spectrophotometric Method. J. Ocean Univ. China 11, 323–330. doi:10.1007/s11802-012-1826-9

CrossRef Full Text | Google Scholar

Khan, S. A., Ialyshev, V., Kim, V. V., Iqbal, M., Al Harmi, H., Boltaev, G. S., et al. (2020). Expedited Transition in the Wettability Response of Metal Meshes Structured by Femtosecond Laser Pulses for Oil-Water Separation. Front. Chem. 8, 768. doi:10.3389/fchem.2020.00768

PubMed Abstract | CrossRef Full Text | Google Scholar

Kočanová, Veronika., Cuhorka, Jiří., Dušek, Libor., and Mikulášek, Petr. (2017). 'Application of Nanofiltration for Removal of Zinc from Industrial Wastewater. Desalination Water Treat. 75, 342–347. doi:10.1016/j.saa.2019.117370

CrossRef Full Text | Google Scholar

Lambert, A., Asokan, M., Issac, G., Love, C., and Chyan, O. (2017). Thin-film UV-Vis Spectroscopy as a Chemically-Sensitive Monitoring Tool for Copper Etching bath. J. Ind. Eng. Chem. 51, 44–48. doi:10.1016/j.jiec.2017.03.004

CrossRef Full Text | Google Scholar

Lee, J.-Y., Oh, J. Y., Putri, K. Y., Baik, M. H., and Yun, J.-I. (2017). Redox Behaviors of Fe(II/III) and U(IV/VI) Studied in Synthetic Water and KURT Groundwater by Potentiometry and Spectroscopy. J. Radioanal. Nucl. Chem. 312, 221–231. doi:10.1007/s10967-017-5233-y

CrossRef Full Text | Google Scholar

Lepane, V., Depret, L., Väli, A.-L., and Suursööt, K. (2015). Impact of Seasonal Climate Change on Optical and Molecular Properties of River Water Dissolved Organic Matter by HPLC-SEC and UV-Vis Spectroscopy. Chem. Biol. Technol. Agric. 2, 1–7. doi:10.1186/s40538-015-0040-6

CrossRef Full Text | Google Scholar

Li, B., Wang, X., Wei, Y., Wang, H., and Barati, M. (2018). Extraction of Copper from Copper and Cadmium Residues of Zinc Hydrometallurgy by Oxidation Acid Leaching and Cyclone Electrowinning. Minerals Eng. 128, 247–253. doi:10.1016/j.mineng.2018.09.007

CrossRef Full Text | Google Scholar

Li, Z.-x., Chen, Y.-f., Zhou, Z.-w., Nie, Y.-z., Xia, Q.-l., Wang, D.-w., et al. (2017). Creation of Skyrmion through Resonance Excitation. J. Magnetism Magn. Mater. 433, 216–221. doi:10.1016/j.jmmm.2017.03.019

CrossRef Full Text | Google Scholar

Liu, P., Nie, Y.-z., Xia, Q.-l., and Guo, G.-h. (2017). Structural and Electronic Properties of Arsenic Nitrogen Monolayer. Phys. Lett. A 381, 1102–1106. doi:10.1016/j.optcom.2017.09.04610.1016/j.physleta.2017.01.026Nie

CrossRef Full Text | Google Scholar

Luo, J., Duan, N., Xu, F., Jiang, L., Zhang, C., and Ye, W. (2019). System-level Analysis of the Generation and Distribution for Pb, Cu, and Ag in the Process Network of Zinc Hydrometallurgy: Implications for Sustainability. J. Clean. Prod. 234, 755–766. doi:10.1016/j.jclepro.2019.06.250

CrossRef Full Text | Google Scholar

Molognoni, D., Chiarolla, S., Cecconet, D., Callegari, A., and Capodaglio, A. G. (2018). Industrial Wastewater Treatment with a Bioelectrochemical Process: Assessment of Depuration Efficiency and Energy Production. Water Sci. Technol. A J. Int. Assoc. Water Pollut. Res. 77, 134–144. doi:10.1007/s10812-009-9224-910.2166/wst.2017.532

CrossRef Full Text | Google Scholar

Rastogi, S. D., Dixit, S., Tripathi, A., and Das, M. (2015). Simultaneous Determination of Acetaminophen and Synthetic Color(s) by Derivative Spectroscopy in Syrup Formulations and Validation by HPLC: Exposure Risk of Colors to Children. AAPS PharmSciTech 16, 505–517. doi:10.1208/s12249-014-0228-2

PubMed Abstract | CrossRef Full Text | Google Scholar

Rote, A. R., and Bari, P. D. (2009). Ratio Spectra Derivative and Zero-Crossing Difference Spectrophotometric Determination of Olmesartan Medoxomil and Hydrochlorothiazide in Combined Pharmaceutical Dosage Form. AAPS PharmSciTech 10, 1200–1205. doi:10.1208/s12249-009-9318-y

PubMed Abstract | CrossRef Full Text | Google Scholar

Walash, M. I., El-Brashy, A., El-Enany, N., and Kamel, M. E. (2009). Second-Derivative Synchronous Fluorescence Spectroscopy for the Simultaneous Determination of Fluphenazine Hydrochloride and Nortriptyline Hydrochloride in Pharmaceutical Preparations. J. Fluoresc 19, 891–904. doi:10.1007/s10895-009-0488-5

CrossRef Full Text | Google Scholar

Yadav, D., and Banerjee, R. (2018). A Comparative Life Cycle Energy and Carbon Emission Analysis of the Solar Carbothermal and Hydrometallurgy Routes for Zinc Production. Appl. Energ. 229, 577–602. doi:10.1016/j.apenergy.2018.08.001

CrossRef Full Text | Google Scholar

Zahmatkesh, M., Spanjers, H., and van Lier, J. B. (2017). 'Fungal Treatment of Humic-Rich Industrial Wastewater: Application of white Rot Fungi in Remediation of Food-Processing Wastewater. Environ. Technol. 38, 1–11. doi:10.1016/j.ijms.2017.01.00610.1080/09593330.2016.1276969

PubMed Abstract | CrossRef Full Text | Google Scholar

Zhang, F., Yang, C., Zhou, X., and Zhu, H. (2018). Fractional Order Fuzzy PID Optimal Control in Copper Removal Process of Zinc Hydrometallurgy. Hydrometallurgy 178, 60–76. doi:10.1016/j.hydromet.2018.03.021

CrossRef Full Text | Google Scholar

Zhou, F., Li, C., Zhu, H., and Li, Y. (2019). Determination of Trace Ions of Cobalt and Copper by UV-Vis Spectrometry in Purification Process of Zinc Hydrometallurgy. Optik 184, 227–233. doi:10.1016/j.ijleo.2019.03.056

CrossRef Full Text | Google Scholar

Zhou, W., Zhao, C., and Guo, J. (2009). The Study of Improving Kalman Filters Family for Nonlinear SLAM. J. Intell. Robot Syst. 56, 543–564. doi:10.1007/s10846-009-9327-9

CrossRef Full Text | Google Scholar