Startseite Optimization of microwave-assisted manganese leaching from electrolyte manganese residue
Artikel Open Access

Optimization of microwave-assisted manganese leaching from electrolyte manganese residue

  • Jun Chang EMAIL logo , Chandrasekar Srinivasakannan , Xianxiu Sun und Fukang Jia
Veröffentlicht/Copyright: 15. September 2019
Veröffentlichen auch Sie bei De Gruyter Brill

Abstract

The process optimization of microwave assisted leaching of manganese from electrolytic manganese residue (EMR) was conducted. The Box-Behnken design (BBD) was utilized to determine the number of experiments as well as to assess the effect of the main leaching parameters, including the reaction temperature, reaction time, concentration of sulfuric acid and dosage of citric acid. A quadratic model was found to best fit the experimental data and was utilized to optimize the process parameters to maximize the percentage manganese recovery. 3-D response surface plots and contour plots were generated utilizing mathematical models to understand the effect of variables as well as to identify the optimal conditions. The optimum conditions of microwave assisted leaching were: temperature of 76°C, time of 55 min, H2SO4 concentration of 0.76 mol·L-1, dosage of citric acid of 3.51 mg/g. Under these conditions, the percentage manganese recovery higher than 90% could be achieved.

1 Introduction

Electrolytic manganese residue (EMR) is a one of the industrial solid waste generated in manganese hydrometallurgical processing, usually contains manganese and ammonia nitrogen [1]. Since 2000, China has become the largest electrolytic manganese metal producing country, representing 98% of the world’s manganese metal output in 2017. Generally, producing 1 ton of manganese would generate 6-10 tons of EMR depending on the grade of manganese ore [2]. In China, currently more than 10 million tons per year of EMR are being discarded as solid waste pile up which result in massive land resources occupied and serious environmental risks. There is an increasing attention on recycling valuable resources from electrolytic manganese residue to overcome environmental concerns in recent years. As high as 4-7% w/w of manganese element remained in EMR [3], therefore the development of efficient treatment technologies for the recovery of manganese from EMR is essential [4].

The EMR contains gangue minerals which engulf a proportion of the manganese compounds [5], thereby reducing the extraction efficiency and therefore these require removal. Recent efforts to improve this include hot sulfuric acid leaching [6], bioleaching [7,8], intensified leaching by electric field [1,3,9], ultrasonically assisted leaching [10,11]. However these are typically associated with shortcomings including long operating times, high costs, complicated processes etc. for manganese recovery.

The application of microwave assisted leaching technology in metallurgy and mineral extraction has been widely reported over the past decades [12]. Selective mineral liberation, controllable and faster heating process, are the main driving force for microwave heating being attractive in extractive industries, usually considered as an efficient and greener technique [13,14]. Studies on extraction of metals from industrial residues using microwave energy have shown it to be significantly faster and in some cases, resulted in enhanced metal dissolution as compared to conventional heating technologies [15, 16, 17, 18]. However [19], enhanced extraction of manganese from EMR using a combination of microwave irradiation and citric acid leaching was rarely reported.

At present, the most commonly used experimental design methods are orthogonal design and uniform design, both of which adopt linear mathematical model to fit data, requiring less experiments but poor predictability. Response Surface Methodology (RSM) is by far the most popular statistical and mathematical tool since it has some functions include experimental design, modeling, model detection, statistical analysis and so on, the optimum level of each factor and interactions among parameter can be identified through RSM [20]. There are three types of response surface design methods, including Central Composite Design, Box-Behnken Design and Plackett-Burman Designs. In particular, the Box-Behnken Design (BBD) is used widely in establishing the second-order RSM, and is one the most popular experimental designs used for process variables [21].

Thus, in order to improve leaching efficiency and to reduce sulfuric acid consumption, the optimization of Mn extraction from EMR using microwave assisted leaching with citric acid using RSM is attempted in the present work. Parameters such as temperature, duration, H2SO4 concentration, dosage of citric acid were assessed using statistical design Box-Behnken method.

2 Materials and methods

2.1 Materials

The EMR used in this work was supplied from Guizhou Wuling Manganese Industry Co. Ltd., and before use its composition was analysed by X-ray fluorescence (XRF, XRF-1800, Shimadzu, Japan), with the results presented in Table 1. The results show the main constituents to be SiO2, SO3, Al2O3, CaO and Fe2O3amounting to approximately 98% of the total composition.

Table 1

The main constituents of EMR used in this study.

CompoundSiO2SO3CaOAl2O3MnOFe2O3K2OMgO
Weight%29.7429.5914.716.866.475.852.721.86

Figure 1 shows the XRD pattern of the EMR (D/Max 2200, Rigaku, Japan), indicates presence of quartz (SiO2), gypsum (CaSO4·2H2O), groutite (Mn3+O(OH)), ammonium iron sulfate (NH4)3Fe(SO4)3, jacobsite (MnFe2O4) as the major minerals. The particle size distribution of the EMR is presented in Figure 2 (Master Sizer 2000, Malvern, UK.). It can be seen the average particle size of EMR is 21 μm and that 90% of the particles are smaller than 47 μm while 10% are smaller than 10 μm.

Figure 1 X-ray diffraction pattern of EMR.
Figure 1

X-ray diffraction pattern of EMR.

Figure 2 Grain size distribution curves of EMR.
Figure 2

Grain size distribution curves of EMR.

2.2 Experimental procedure and apparatus

The leaching tests were carried out in a self-made microwave reactor which had a temperature and stirring speed control system (Figure 3).

Figure 3 Schematic diagram of microwave reactor (1 – reflux condenser, 2 – three-necked flask, 3 – mechanically controlled stirrer, 4 – stirring controller, 5 – digital thermometer, 6 – LCD screen, 7 – temperature setting knob, 8 – power switch, 9 – emergency switch, 10 – microwave power setting knob).
Figure 3

Schematic diagram of microwave reactor (1 – reflux condenser, 2 – three-necked flask, 3 – mechanically controlled stirrer, 4 – stirring controller, 5 – digital thermometer, 6 – LCD screen, 7 – temperature setting knob, 8 – power switch, 9 – emergency switch, 10 – microwave power setting knob).

First, the sulfuric acid solution was poured into a three-necked 500 mL flask reactor. Then, a certain amount of EMR sample was added to it. Following this, the flask was placed into the microwave reactor and the temperature raised to the desired value. The agitation speed and microwave power were kept constant at 300 rpm and 200 W respectively for all experiments. After the required duration was met and the solid and liquid separated, the concentration of manganese in filter liquor was determined by atomic absorption spectrometry (Z2000HITACHI). The percentage of manganese leached (Em) was calculated according to the following equation:

(1)Em=cV/M0×100%

where c and M0 are the mass of Mn in the leaching solution and the original sample, respectively; V is the volume of the leaching solution after filtration.

2.3 Experimental design

At present work, four important parameters such as leaching temperature (X1, °C), leaching duration (X2, min), H2SO4 concentration (X3, mol·L−1), and dosage of citric acid (X4, mL/g) were chosen as the independent variables. The low, middle, and high levels of each variable were identified as −1, 0, and +1 (Table 2).

Table 2

Levels and codes used in Box-Behnken design.

SymbolCoded level
VariableUncodedCodedLowCenterHigh
–101
Temperature (°C)Χ1A406080
Time (min)Χ2B204060
H2SO4 concentration (mol·L−1)Χ3C0.20.50.8
Dosage of citric acid (mg/g)X4D2610

The above stated upper and lower limits of the variables were selected based on preliminary experiments in addition to information gathered from literature sources. In order to evaluate the effects of independent variables on percentage of Mn extracted, batch tests were carried out. The coded values of the four significant parameters were generated based on Eq. 2:

(2)xi=XiX0ΔXi

where xi is defined to be a dimensionless value of an independent variable, Xi is the real value of variable, X0 is the real value of an independent factor at the center point, and ΔXi is the step change.

The statistical models and data analysis were given using Design-Expert 8.0.6 software (trial version). The design is depended on the combination of 2k factorial design with an incomplete block design. Total numbers of experiments required in a Box-Behnken design can be calculated according to the Eq. 3 [21]:

(3)N=2k(k-1)+cp

where N is the number of experiments, k is the factor number (k = 4), and (cp) is the replicate number of the central point. It resulted in 24 experiments with three repetitions at the center point to estimate the pure error. The generalized form of model equation relating the X’s and Y is given by Eq. 4:

(4)Y=β0+i=1kβiXi+i=1kβiiXi2ii<1kjkβijXiXj++e

where Y is the response, β0 is a constant coefficient, Xi and Xj are the input factors, βi, βii and βij are linear, quadratic and interaction coefficients, respectively, e is the random error. The quality of the fit of the model would be evaluated by ANOVA.

3 Results and discussion

3.1 Data analysis

The number of experiments generated utilizing Box-Behnken design are listed in Table 3, which comprehensively provides the process conditions at which experiments were conducted along with the outcome of the experiment ‘Percentage Mn recovery’.

Table 3

Box-Behnken experimental design and response value.

Std No.Coded level of variablesActual level of variablesObserved
ABCDX1X2X3X4recovery (%)
1–1–10040200.5665.02
21–10080200.5682.53
3–110040600.5673.23
4110080600.5693.61
500–1–160400.2267.95
6001–160400.8283.18
700–1160400.21072.67
8001160400.81089.04
9–100–140400.5269.89
10100–180400.5284.77
11–100140400.51070.42
12100180400.51093.66
130–1–1060200.2665.54
1401–1060600.2669.13
150–11060200.8678.65
16011060600.8691.08
17–10–1040400.2664.24
1810–1080400.2671.58
19–101040400.8669.22
20101080400.8692.78
210–10–160200.5277.05
22010–160600.5285.32
230–10160200.51080.57
24010160600.51092.04
25000060400.5688.97
26000060400.5688.08
27000060400.5689.91

Different empirical models were attempted to relate the process variables and independent variable subjecting it to statistical analysis. Among the models tested the quadratic model was found to be the best and the regression model is expressed as Eq. 5:

(5)Y=22.02+1.86X1+0.62X2+64.37X3+0.15X4+1.79×103X1X2+0.68X1X3+0.03X1X4+0.37X2X3+0.01X2X4+0.24X3X40.02X129.34×103X2295.29X320.13X42

where Y is the percentage Mn extraction, A is the reaction temperature, B is the reaction time, C is the H2SO4 concentration, D is the dosage of citric acid.

The adequacy of model to utilize the statistical methods was established by using diagnostic plot (normal % probability versus studentized residuals, studentized residuals versus run number). The probablity plot authenticates data to be considered as of normal distributed while the studentize plot helps to identify the outliers.

Figure 4a shows all the data falling on line except one authenticating that the sample data is from a normally distributed population. Figure 4b shows possibility of the one of the data could be an outlier. Figure 4c authenticates the validity of the model equation (Eq. 5), as the model prediction is very close to the experimental data [22]. The adequacy of the model was investigated using the sequential model sum of squares and the model summary statistics are illustrated in Table 4.

Figure 4 Diagnostic plot the model for manganese leaching: (a) normal % probability versus studentized residuals, (b) studentized residuals versus run number, (c) predicted versus actual data.
Figure 4

Diagnostic plot the model for manganese leaching: (a) normal % probability versus studentized residuals, (b) studentized residuals versus run number, (c) predicted versus actual data.

Table 4

Adequacy of the model.

SourceSum of SquaresDegree of freedomMean SquareF-valuep-value Prob > FRemarks
Mean vs Total1.712 × 10511.712 × 10517.46------
Linear vs Mean1999.504499.870.55< 0.0001
2FI vs Linear107.73617.9552.480.7629
Quadratic vs 2FI493.804123.451.37< 0.0001Suggested
Cubic vs Quadratic20.6882.58----0.4042Aliased
Residual7.5541.89----
SourceStd. Dev.R-SquaredAdjustedPredictedPRESS
R-SquaredR-Squared
Linear5.350.76050.71690.6723861.49
2FI5.710.80150.67740.56291149.15
Quadratic1.530.98930.97670.9404156.72Suggested
Cubic1.370.99710.98130.6766850.18Aliased

As seen from Table 4, the value of regression coefficient for quadratic model is 0.9893. The R2adjand predicted R2 are 0.9767 and 0.9404 for the quadratic model, respectively. The high R2 shows the proximity of the model prediction to the experimental data. In general, the difference between adjusted R2 and predicted R2 is considered to be good fitness within the range of 0~0.200 for the model [23]. At present work, the difference between the predicted R2 and the adjusted R2 for the given quadratic mode is only 0.0363. Adequate precision is a crucial criterion to judge the signal to noise ratio. A ratio greater than 4 is preferable, and the ratio of 29.122 (adequate precision) indicates an adequate signal [24]. Based on all the favorable facts detailed above it can be concluded that the model adequately fits the experimental data.

Table 5 shows the analysis results obtained from the ANOVA test for fitting quadratic model. The Model F-value 78.98 implies that the model is significant. There is only a 0.01% chance that such a large “Model F-value” will appear due to noise.

Table 5

Regression analysis of BBD criterion data for leaching of manganese.

SourceSum of SquaresDegree of freedomMean SquareF-valuep-value Prob. > FSignificance
Model2601.0314185.7978.98< 0.0001Significant
A952.481952.48404.90< 0.0001Significant
B252.541252.54107.36< 0.0001Significant
C718.271718.27305.34< 0.0001Significant
D76.20176.2032.390.0001Significant
AB2.0612.060.880.3679
AC65.77165.7727.960.0002Significant
AD17.47117.477.430.0184Significant
BC19.54119.548.300.0138Significant
BD2.5612.561.090.3174
CD0.3210.320.140.7166
A2231.621231.6298.46< 0.0001Significant
B274.50174.5031.670.0001Significant
C2392.281392.28166.76< 0.0001Significant
D224.40124.4010.370.0073Significant
Residual28.23122.35----------
Lack of Fit26.55102.663.170.2635Not significant
Pure Error1.6720.84----------
Cor Total2629.2626---------------

The significance of each coefficient was investigated based on F-test and P-test also as shown in Table 5. According to the F values of A, B, C and D, the influence degree of the four variables on manganese extraction by microwave assisted leaching are illustrated in Table 6.

Table 6

Significance rank of different factors on manganese extraction under microwave heating.

RankParameters
1Temperature
2H2SO4 concentration
3Time
4Dosage of citric acid

A values of “Prob > F” less than 0.0500 imply proposed model is significant, while a values greater than 0.1000 indicate the proposed model is non-significant [25]. In this case A, B, C, D, AC, AD, BC, A2, B2, C2, D2 are significant model terms. It indicates the linear effects and square effects of temperature, H2SO4 concentration, dosage of citric acid and time are significant. In addition, the interactive effects of temperature and H2SO4 concentration (P = 0.0002), temperature and dosage of citric acid (P = 0.0184) and time and H2SO4 concentration (P = 0.0138) have an adequate influence on the extraction of manganese by microwave assisted leaching. Compared to the value of pure error, the “Lack of Fit F-value” of 3.17 indicates that the Lack of Fit is not significant. At the same time, there is a 26.35% chance that a “Lack of Fit F-value” this large could appear owing to noise, non-significant lack of fit is desired to ensure the high quality of the fit of the model [26].

3.2 Contour plots and response surface

The effects of variables on the manganese leaching efficiency is assessed by plotting 3D surface curves against any two independent variables, while keeping other variables at their center value. The 3D response surface plots and the contour plots from the interactions between the variable are shown in Figures 5 and 6.

Figure 5 Response surface plots show the effect of temperature (X1), time (X2), H2SO4 concentration (X3) and dosage of citric acid (X4) on % manganese extraction with microwave irradiation.
Figure 5

Response surface plots show the effect of temperature (X1), time (X2), H2SO4 concentration (X3) and dosage of citric acid (X4) on % manganese extraction with microwave irradiation.

Figure 6 Contour plots show the effect between temperature (X1), time (X2), H2SO4 concentration (X3) and dosage of citric acid (X4) on manganese extraction.
Figure 6

Contour plots show the effect between temperature (X1), time (X2), H2SO4 concentration (X3) and dosage of citric acid (X4) on manganese extraction.

Figure 5a demonstrates the combined effect of temperature with reaction time. It is clear from Figure 5a that % leaching increases significantly with increasing temperature. An increase in temperature from 40°C to 80°C increased the percentage leaching remarkably from 65.02% to 93.61%. The corresponding contour plot is shown in Figure 6a The combination of the response surface along with the contour plot helps to identify the combination of time and temperature that could provide the maximum percentage recovery. The combined factors reach an asymptote at % Mn recovery higher than 90%. An increase in the percentage Mn extraction with increase in temperature could be attributed to the higher rates of mass transfer due to increased diffusion coefficient. While an increase with increase in time could be due to the time available to complete the extraction.

Figure 5b shows the combined effect of H2SO4 concentration and leaching temperature on the % leaching. As can be seen from Figure 5b manganese recovery increased with increasing both: temperature and H2SO4 concentration. However, at higher H2SO4 concentration effect of temperature on the percent recovery of Mn was significant, while at lower H2SO4 concentration only a minor effect was observed. An increase in the concentration of H2SO4 would increase the rate of reaction and due to reduced the mass transfer resistance aiding diffusion of H2SO4 to the site of Mn containing mineral phase, facilitating higher % leaching. Figures 5b and 6b help to identify the combination of factors that maximize the % Mn recovery.

Figure 5c illustrates the combined effect of citric acid dose with temperature. The effect of increase in citric acid concentration seems to be insignificant at low temperatures while at high temperatures it exhibits an increase with increase in concentration. Again, Figures 5c and 6c provide the combination factors that offer the maximum of % Mn recovery.

Figures 5d and 5e show the effect of H2SO4 and citric acid dose in combination with time on the percentage manganese recovery respectively. The effect of these parameters was discussed in detail earlier. The combination of H2SO4 concentration as well as time is found to have significant influence on the percentage Mn recovery while the combination of the citric acid dose and the time has only marginal effect on the percentage Mn recovery. Figures 6d and 6e provide the combination of factors that could maximize the % Mn recovery [27].

The interactive effect of H2SO4 concentration with citric acid dose is shown in Figure 5f It can be observed that an increase in both H2SO4 concentration as well as citric acid dose increases the percentage leaching. An increase in the amount of sulfuric acid affects the dissolution rate of manganese in leaching of EMR much more than the citric acid dose. Although the increase in the citric acid dose doesn’t seem to increase the extraction rate significantly, the increase in citric acid dose promotes conversion of high valence of Mn into low valence of Mn, inhibiting the leaching of other gangue minerals. In other words, citric acid offers not only high manganese recovery and selectivity of leaching but also contributes to reduced acid consumption rendering the process more environmentally benign. Above mentioned result is also revealed by the corresponding contour plots presented in Figure 6f

3.3 Optimization

Although the effect of process variables and combinations thereof that could maximize the percentage Mn recovery is evident from plots developed, the optimal combination of factors that would maximize the percentage recovery may be identified with the help of process optimization. Within the range of parameters assessed in the present work, the process optimizer identified the optimal conditions to maximize the percentage Mn recovery as a temperature of 77°C, time of 55 min, H2SO4 concentration of 0.76 mol·L-1, dosage of citric acid of 3.51 mg/g, corresponding to a maximum Mn recovery of 94.25% with the desirability of 1. The pictorial representation of the optimized process parameters as shown the software is provided in Figure 7.

Figure 7 Ramps of the numerical optimization.
Figure 7

Ramps of the numerical optimization.

In order to verify the results of predicted optimum conditions and understand the role of microwave irradiation, the experiments were carried out at identified optimized process conditions under conventional heating and microwave fields, the results are shown in Table 7.

Table 7

The main constituents of EMR (wt%) after leaching with different methods.

MethodSiO2SO3CaOAl2O3MnOFe2O3K2OMgO
Conventional heating33.2026.0315.687.763.327.343.231.02
Microwave assisted leaching37.2032.4013.497.830.442.473.510.74

Table 7 revealed that about a half of the manganese retain in the leached residue under conventional leaching process. On the contrary, microwave-assisted leaching ensures the perfect recovery of manganese from EMR. This can be explained that the different microwave absorber character between manganese-bearing mineral and other components result in intergranular and transgranular thermal stress cracking, increasing the contact area between lixiviant and ores. Therefore, microwave-assisted leaching led to the higher recovery efficiency. Moreover, the experiment at identified optimized process condition was carried out in triplicates and the average value of 93.28% for Mn leaching efficiency is sufficiently agree with the predicted value. Hence, this validation confirms the adequacy of the developed quadratic model for Mn leaching.

4 Conclusion

In the present work, the effect of temperature, time, concentration of sulphuric acid and dosage of citric acid were assessed to identify the optimal conditions to maximize the percentage Mn recovery from EMR using BBD of RSM. The proposed quadratic model was used successfully to fit the experimental data, with high values of R2 and R2adjof 0.9767 and 0.9404, respectively. ANOVA showed that the effect of temperature and concentration of H2SO4 to be the most significant parameters a compare dot time and dosage of critic acid. The best conditions for manganese leaching were identified to be a temperature of 76°C, time of 55 min, H2SO4 concentration of 0.76 mol·L-1, dosage of citric acid of 3.51 mg/g with the maximum % Mn recovery being 94.25%. With microwave assisted leaching the manganese leaching rate was about 40% higher than that found with conventional leaching. The high recovery at favorable process conditions economically favor the process for scale-up and eventual commercial adoption.

Acknowledgments

Authors appreciate the valuable comments from Kathryn Mumford (an associate professor in the Department of Chemical and Biomolecular Engineering at The University of Melbourne). This work was financially supported by the National Natural Science Foundation of China (No. 51804220 and 51864042), the Scientific Elitists Supporting Project of Department of Education of Guizhou Province (No. KY[2017]090), the Joint Fund Project of Science and technology department of Guizhou province (No. LH[2017]7312), the Basic Research Project of Guizhou Province (No. [2019]1311) and CSC scholarship (File No. 201708525070).

  1. Conflict of interest

    Conflict of interest statement: The authors declare no conflict of interest.

References

[1] Shu J.C., Liu R.L., Liu Z.H., Du J., Tao C.Y., Electrokinetic remediation of manganese and ammonia nitrogen from electrolytic manganese residue. Environ. Sci. Pollut. R., 2015, 22, 16004-16013.10.1007/s11356-015-4817-8Suche in Google Scholar PubMed

[2] Shu J.C., Liu R.L., Liu Z.H., Chen H.L., Du J., Tao C.Y., Solidification/stabilization of electrolytic manganese residue using phosphate resource and low-grade MgO/CaO. J. Hazard. Mater., 2016, 317, 267-274.10.1016/j.jhazmat.2016.05.076Suche in Google Scholar PubMed

[3] Shu J.C., Liu R.L., Liu Z.H., Chen H.L., Tao C.Y., Enhanced extraction of manganese from electrolytic manganese residueby electrochemical. J. Electroanal. Chem., 2016, 780, 32-37.10.1016/j.jelechem.2016.08.033Suche in Google Scholar

[4] Li C.X., Zhong H., Wang S., Xue J.R., Leaching behavior and risk assessment of heavy metals in a landfill of electrolytic manganese residue in Western Hunan, China. Hum. Ecol. Risk Assess., 2014, 20(5), 1249-1263.10.1080/10807039.2013.849482Suche in Google Scholar

[5] Chen H.L., Differences analysis of minerals compositions and toxicity characteristics between the fresh electrolytic manganese residue and the stockpiling residue. Journal of Guizhou Normal University (Natural Science), 2016, 34, 32-36 (in Chinese).Suche in Google Scholar

[6] Olívia S.H.S., Cornelio F.C., Gilmare A.S., Gláudio G.S., Manganese ore tailing: Optimization of acid leaching conditions and recovery of soluble manganese. J. Environ. Manage., 2015, 147, 314-320.10.1016/j.jenvman.2014.09.020Suche in Google Scholar PubMed

[7] Duan N., Zhou C.B., Chen B., Jiang W.F., Xin B.P., Bioleaching of Mn from manganese residues by the mixed culture of Acidithiobacillus and mechanism. J. Chem. Technol. Biot., 2011, 86, 832-837.10.1002/jctb.2596Suche in Google Scholar

[8] Xin B.P., Chen B., Duan N., Zhou C.B., Extraction of manganese from electrolytic manganese residue by bioleaching. Bioresource Technol., 2011, 102, 1683-1687.10.1016/j.biortech.2010.09.107Suche in Google Scholar PubMed

[9] Zhang X.R., Liu Z.H., Wu X.B., Du J., Tao C.Y, Electric field enhancement in leaching of manganese from low-grade manganese dioxide ore: Kinetics and mechanism study. J. Electroanal. Chem., 2017, 788, 165-174.10.1016/j.jelechem.2017.02.009Suche in Google Scholar

[10] Li H., Zhang Z.H., Tang S.P., Li Y.N, Zhang Y.K., Ultrasonically assisted acid extraction of manganese from slag. Ultrason. Sonochem., 2008, 15, 339-343.10.1016/j.ultsonch.2007.07.010Suche in Google Scholar PubMed

[11] OuYang Y.Z., Peng X.W., Cao J.B., Li Z.P., Deng X.D., Ultrasonic leaching of electrolytic manganese residue with additive. Environmental Protection of Chemical Industry, 2007, 27, 257-259 (in Chinese).Suche in Google Scholar

[12] Chang J., Zhang L.B., Yang C.J, Ye Q.X, Chen J., Peng J.H., et al., Kinetics of microwave roasting of zinc slag oxidation dust with concentrated sulfuric acid and water leaching. Chem. Eng. Process., 2015, 97, 75-83.10.1016/j.cep.2015.09.006Suche in Google Scholar

[13] Liu B.G., Peng J.H., Zhang L.B., Zhou J.W., Srinivasakannan C., Preparation of V2O5 from ammonium metavanadate via microwave intensification. Russ. J. Non-Ferr. Met., 2017, 58, 600-607.10.3103/S1067821217060062Suche in Google Scholar

[14] Pinto I.S.S., Soares H.M.V.M., Microwave-assisted selective leaching of nickel from spent hydrodesulphurization catalyst: A comparative study between sulphuric and organic acids. Hydrometallurgy, 2013, 140, 20-27.10.1016/j.hydromet.2013.08.009Suche in Google Scholar

[15] Wen T., Zhao Y.L., Xiao Q.H., Ma Q.L., Kang S.C., Li H.Q., et al., Effect of microwave assisted heating on chalcopyrite leaching of kinetics, interface temperature and surface energy. Results Phys., 2017, 7, 2594-2600.10.1016/j.rinp.2017.07.035Suche in Google Scholar

[16] Suoranta T., Zugazua O., Niemelä M., Perämäki P., Recovery of palladium, platinum, rhodium and ruthenium from catalyst materials using microwave-assisted leaching and cloud point extraction. Hydrometallurgy, 2015, 154, 56-62.10.1016/j.hydromet.2015.03.014Suche in Google Scholar

[17] Maryam S.S., Vanpeteghem G., Neto I.F., Soares H.M., Selective leaching of Zn from spent alkaline batteries using environmentally friendly approaches. Waste Manage., 2017, 60, 696-705.10.1016/j.wasman.2016.12.002Suche in Google Scholar PubMed

[18] Kim E., Horckmans L., Spooren J., Selective leaching of Pb, Cu, Ni and Zn from secondary lead smelting residues. Hydrometallurgy, 2017, 169, 372-381.10.1016/j.hydromet.2017.02.027Suche in Google Scholar

[19] Astuti W., Hirajima T., Sasaki K., Okibe N., Comparison of effectiveness of citric acid and other acids in leaching of low-grade Indonesian saprolitic ores. Miner. Eng., 2016, 85, 1-16.10.1016/j.mineng.2015.10.001Suche in Google Scholar

[20] Shaghaghi-Moghaddam R., Jafarizadeh-Malmiri H., Mehdikhani P., Alijanianzadeh R., Jalalian S., Optimization of submerged fermentation conditions to overproduce bioethanol using two industrial and traditional Saccharomyces cerevisiae strains. Green Process. Synth., 2019, 8(1), 157-162.10.1515/gps-2018-0044Suche in Google Scholar

[21] Tanong K., Coudert L., Mercier G., Blais J.F., Recovery of metals from a mixture of various spent batteries by a hydrometallurgical process. J. Environ. Manage., 2016, 181, 95-107.10.1016/j.jenvman.2016.05.084Suche in Google Scholar PubMed

[22] Saikia R., Goswami R., Bordoloi N., Senapati K. K., Pant K. K., Kumar M., et al., Removal of arsenic and fluoride from aqueous solution by biomass based activated biochar: optimization through response surface methodology. J. Environ. Chem. Eng., 2017, 5, 5528-5539.10.1016/j.jece.2017.10.027Suche in Google Scholar

[23] Jiang H.L., Yang J.L., Shi Y.P., Optimization of ultrasonic cell grinder extraction of anthocyanins from blueberry using response surface methodology. Ultrason. Sonochem., 2017, 34, 325-331.10.1016/j.ultsonch.2016.06.003Suche in Google Scholar

[24] Liu H., Zhang Y.M., Huang J., Liu T., Xue N.N., Shi Q.H., Optimization of vanadium (IV) extraction from stone coal leaching solution by emulsion liquid membrane using response surface methodology. Chem. Eng. Res. Des., 2017, 123, 111-119.10.1016/j.cherd.2017.05.001Suche in Google Scholar

[25] Nazari E., Rashchi F., Saba M., Mirazimi S.M.J., Simultaneous recovery of vanadium and nickel from power plant fly ash: Optimization of parameters using response surface methodology. Waste Manage., 2014, 34, 2687-2696.10.1016/j.wasman.2014.08.021Suche in Google Scholar

[26] Kul M., Oskay K.O., Şimşir M., Sübütay H., Kirgezen H., Optimization of selective leaching of Zn from electric arc furnace steelmaking dust using response surface methodology. T. Nonferr. Metal. Soc., 2015, 25, 2753-2762.10.1016/S1003-6326(15)63900-0Suche in Google Scholar

[27] Madakkaruppana V., Piusb A., Sreenivas T., Giri N., Sarbajna C., Influence of microwaves on the leaching kinetics of uraninite from a low grade ore in dilute sulfuric acid. J. Hazard. Mater., 2016, 313, 9-17.10.1016/j.jhazmat.2016.03.050Suche in Google Scholar PubMed

Received: 2019-04-02
Accepted: 2019-07-08
Published Online: 2019-09-15

© 2020 Chang et al., published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 International License.

Artikel in diesem Heft

  1. Obituary for Prof. Dr. Jun-ichi Yoshida
  2. Regular Articles
  3. Optimization of microwave-assisted manganese leaching from electrolyte manganese residue
  4. Crustacean shell bio-refining to chitin by natural deep eutectic solvents
  5. The kinetics of the extraction of caffeine from guarana seed under the action of ultrasonic field with simultaneous cooling
  6. Biocomposite scaffold preparation from hydroxyapatite extracted from waste bovine bone
  7. A simple room temperature-static bioreactor for effective synthesis of hexyl acetate
  8. Biofabrication of zinc oxide nanoparticles, characterization and cytotoxicity against pediatric leukemia cell lines
  9. Efficient synthesis of palladium nanoparticles using guar gum as stabilizer and their applications as catalyst in reduction reactions and degradation of azo dyes
  10. Isolation of biosurfactant producing bacteria from Potwar oil fields: Effect of non-fossil fuel based carbon sources
  11. Green synthesis, characterization and photocatalytic applications of silver nanoparticles using Diospyros lotus
  12. Dielectric properties and microwave heating behavior of neutral leaching residues from zinc metallurgy in the microwave field
  13. Green synthesis and stabilization of silver nanoparticles using Lysimachia foenum-graecum Hance extract and their antibacterial activity
  14. Microwave-induced heating behavior of Y-TZP ceramics under multiphysics system
  15. Synthesis and catalytic properties of nickel salts of Keggin-type heteropolyacids embedded metal-organic framework hybrid nanocatalyst
  16. Preparation and properties of hydrogel based on sawdust cellulose for environmentally friendly slow release fertilizers
  17. Structural characterization, antioxidant and cytotoxic effects of iron nanoparticles synthesized using Asphodelus aestivus Brot. aqueous extract
  18. Phase transformation involved in the reduction process of magnesium oxide in calcined dolomite by ferrosilicon with additive of aluminum
  19. Green synthesis of TiO2 nanoparticles from Syzygium cumini extract for photo-catalytic removal of lead (Pb) in explosive industrial wastewater
  20. The study on the influence of oxidation degree and temperature on the viscosity of biodiesel
  21. Prepare a catalyst consist of rare earth minerals to denitrate via NH3-SCR
  22. Bacterial nanobiotic potential
  23. Green synthesis and characterization of carboxymethyl guar gum: Application in textile printing technology
  24. Potential of adsorbents from agricultural wastes as alternative fillers in mixed matrix membrane for gas separation: A review
  25. Bactericidal and cytotoxic properties of green synthesized nanosilver using Rosmarinus officinalis leaves
  26. Synthesis of biomass-supported CuNi zero-valent nanoparticles through wetness co-impregnation method for the removal of carcinogenic dyes and nitroarene
  27. Synthesis of 2,2′-dibenzoylaminodiphenyl disulfide based on Aspen Plus simulation and the development of green synthesis processes
  28. Catalytic performance of the biosynthesized AgNps from Bistorta amplexicaule: antifungal, bactericidal, and reduction of carcinogenic 4-nitrophenol
  29. Optical and antimicrobial properties of silver nanoparticles synthesized via green route using honey
  30. Adsorption of l-α-glycerophosphocholine on ion-exchange resin: Equilibrium, kinetic, and thermodynamic studies
  31. Microwave-assisted green synthesis of silver nanoparticles using dried extracts of Chlorella vulgaris and antibacterial activity studies
  32. Preparation of graphene oxide/chitosan complex and its adsorption properties for heavy metal ions
  33. Green synthesis of metal and metal oxide nanoparticles from plant leaf extracts and their applications: A review
  34. Synthesis, characterization, and electrochemical properties of carbon nanotubes used as cathode materials for Al–air batteries from a renewable source of water hyacinth
  35. Optimization of medium–low-grade phosphorus rock carbothermal reduction process by response surface methodology
  36. The study of rod-shaped TiO2 composite material in the protection of stone cultural relics
  37. Eco-friendly synthesis of AuNPs for cutaneous wound-healing applications in nursing care after surgery
  38. Green approach in fabrication of photocatalytic, antimicrobial, and antioxidant zinc oxide nanoparticles – hydrothermal synthesis using clove hydroalcoholic extract and optimization of the process
  39. Green synthesis: Proposed mechanism and factors influencing the synthesis of platinum nanoparticles
  40. Green synthesis of 3-(1-naphthyl), 4-methyl-3-(1-naphthyl) coumarins and 3-phenylcoumarins using dual-frequency ultrasonication
  41. Optimization for removal efficiency of fluoride using La(iii)–Al(iii)-activated carbon modified by chemical route
  42. In vitro biological activity of Hydroclathrus clathratus and its use as an extracellular bioreductant for silver nanoparticle formation
  43. Evaluation of saponin-rich/poor leaf extract-mediated silver nanoparticles and their antifungal capacity
  44. Propylene carbonate synthesis from propylene oxide and CO2 over Ga-Silicate-1 catalyst
  45. Environmentally benevolent synthesis and characterization of silver nanoparticles using Olea ferruginea Royle for antibacterial and antioxidant activities
  46. Eco-synthesis and characterization of titanium nanoparticles: Testing its cytotoxicity and antibacterial effects
  47. A novel biofabrication of gold nanoparticles using Erythrina senegalensis leaf extract and their ameliorative effect on mycoplasmal pneumonia for treating lung infection in nursing care
  48. Phytosynthesis of selenium nanoparticles using the costus extract for bactericidal application against foodborne pathogens
  49. Temperature effects on electrospun chitosan nanofibers
  50. An electrochemical method to investigate the effects of compound composition on gold dissolution in thiosulfate solution
  51. Trillium govanianum Wall. Ex. Royle rhizomes extract-medicated silver nanoparticles and their antimicrobial activity
  52. In vitro bactericidal, antidiabetic, cytotoxic, anticoagulant, and hemolytic effect of green-synthesized silver nanoparticles using Allium sativum clove extract incubated at various temperatures
  53. The green synthesis of N-hydroxyethyl-substituted 1,2,3,4-tetrahydroquinolines with acidic ionic liquid as catalyst
  54. Effect of KMnO4 on catalytic combustion performance of semi-coke
  55. Removal of Congo red and malachite green from aqueous solution using heterogeneous Ag/ZnCo-ZIF catalyst in the presence of hydrogen peroxide
  56. Nucleotide-based green synthesis of lanthanide coordination polymers for tunable white-light emission
  57. Determination of life cycle GHG emission factor for paper products of Vietnam
  58. Parabolic trough solar collectors: A general overview of technology, industrial applications, energy market, modeling, and standards
  59. Structural characteristics of plant cell wall elucidated by solution-state 2D NMR spectroscopy with an optimized procedure
  60. Sustainable utilization of a converter slagging agent prepared by converter precipitator dust and oxide scale
  61. Efficacy of chitosan silver nanoparticles from shrimp-shell wastes against major mosquito vectors of public health importance
  62. Effectiveness of six different methods in green synthesis of selenium nanoparticles using propolis extract: Screening and characterization
  63. Characterizations and analysis of the antioxidant, antimicrobial, and dye reduction ability of green synthesized silver nanoparticles
  64. Foliar applications of bio-fabricated selenium nanoparticles to improve the growth of wheat plants under drought stress
  65. Green synthesis of silver nanoparticles from Valeriana jatamansi shoots extract and its antimicrobial activity
  66. Characterization and biological activities of synthesized zinc oxide nanoparticles using the extract of Acantholimon serotinum
  67. Effect of calcination temperature on rare earth tailing catalysts for catalytic methane combustion
  68. Enhanced diuretic action of furosemide by complexation with β-cyclodextrin in the presence of sodium lauryl sulfate
  69. Development of chitosan/agar-silver nanoparticles-coated paper for antibacterial application
  70. Preparation, characterization, and catalytic performance of Pd–Ni/AC bimetallic nano-catalysts
  71. Acid red G dye removal from aqueous solutions by porous ceramsite produced from solid wastes: Batch and fixed-bed studies
  72. Review Articles
  73. Recent advances in the catalytic applications of GO/rGO for green organic synthesis
Heruntergeladen am 8.9.2025 von https://www.degruyterbrill.com/document/doi/10.1515/gps-2020-0001/html?lang=de
Button zum nach oben scrollen