Fabrication of Polyethyleneimine-Modified Nanocellulose/Magnetic Bentonite Composite as a Functional Biosorbent for Efficient Removal of Cu(Ⅱ)
Abstract
:1. Introduction
2. Experimental
2.1. Materials
2.2. Synthesis of TOCN
2.3. Synthesis of TOCN–PEI
2.4. Synthesis of Magnetic Bentonite
2.5. Synthesis of PNMBC
2.6. Characterization
2.7. Batch Adsorption Test
3. Results and Discussion
3.1. Characterization of PNMBC
3.1.1. FT-IR Analysis
3.1.2. XRD Analysis
3.1.3. SEM Analysis
3.1.4. TG Analysis
3.1.5. BET Analysis
3.1.6. Zeta Potential
3.2. Effect of Batch Adsorption Performance
3.2.1. Effect of Biosorbent Dosage
3.2.2. Effect of Initial Concentration of Cu(Ⅱ)
3.2.3. Effect of Adsorption Time
3.2.4. Effect of Temperature
3.3. Adsorption Mechanism
3.4. Reusability of PNMBC
4. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Adsorbent | Pollutant | Maximum Adsorption Capacity (mg/g) | Reference |
---|---|---|---|
CMCNFs | Cu(II) | 115.3 | [22] |
PEI-BC | Cu(II) | 148 | [23] |
TOCN–PEI | Cu(II) | 52.32 | [28] |
BC/GO | Cu(II) | 65 | [30] |
cellu/cys-bent | Cu(II) | 32.36 | [39] |
MKC | Cu(II) | 16.5 | [41] |
Fe3O4/ATP@(BCNs/CS) | Cu(II) | 70.5 | [44] |
TCP | Cu(II) | 109.89 | [48] |
PNMBC | Cu(II) | 757.45 | This work |
Composite | Temperature (°C) | Langmuir Models | Freundlich Models | ||||
---|---|---|---|---|---|---|---|
Qmax (mg/g) | KL (L/mg) | R2 | n | KF (mg/g)(L/mg)−1/n | R2 | ||
1:1 | 15 | 2790.02 | 0.00104 | 0.09003 | 1.20 | 5.84 | 0.90881 |
25 | 847.45 | 0.00593 | 0.91955 | 1.96 | 29.31 | 0.93284 | |
35 | 555.55 | 0.0135 | 0.96048 | 2.79 | 57.35 | 0.96510 | |
1:2 | 15 | 1306.5 | 0.00304 | 0.64308 | 1.56 | 16.14 | 0.93969 |
25 | 588.23 | 0.0110 | 0.93572 | 2.51 | 46.37 | 0.95370 | |
35 | 813.01 | 0.00400 | 0.98150 | 1.69 | 15.25 | 0.98320 | |
2:1 | 15 | 1288.95 | 0.00204 | 0.47880 | 1.45 | 9.72 | 0.94024 |
25 | 704.22 | 0.00600 | 0.82663 | 2.31 | 38.94 | 0.94024 | |
35 | 487.80 | 0.00900 | 0.92437 | 2.41 | 33.39 | 0.93280 |
Composite | Temperature (°C) | Pseudo-First-Order Adsorption Kinetics | Pseudo-Second-Order Adsorption Kinetics | ||||
---|---|---|---|---|---|---|---|
K1 (min−1) | Qe (mg/g) | R2 | K2 (g/(mg·min)) | Qe (mg/g) | R2 | ||
1:1 | 15 | 0.102 | 28.20 | 0.55969 | 0.013 | 273.22 | 0.99998 |
25 | 0.14 | 16.82 | 0.60238 | 0.026 | 245.70 | 0.99999 | |
35 | 0.091 | 25.95 | 0.82591 | 0.015 | 190.11 | 0.99998 | |
1:2 | 15 | 0.085 | 11.44 | 0.57244 | 0.033 | 248.76 | 1 |
25 | 0.052 | 21.76 | 0.39796 | 0.014 | 238.09 | 0.99985 | |
35 | 0.049 | 17.84 | 0.42768 | 0.016 | 234.19 | 0.99989 | |
2:1 | 15 | 0.099 | 4.34 | 0.52444 | 0.098 | 211.86 | 1 |
25 | 0.065 | 4.51 | 0.31011 | 0.073 | 215.52 | 1 | |
35 | 0.098 | 21.06 | 0.86403 | 0.019 | 173.31 | 0.99999 |
Composite | ΔG (KJ/mol) | ΔH (KJ/mol) | ΔS (J/mol·K) | ||
---|---|---|---|---|---|
15 °C | 25 °C | 35 °C | |||
1:1 | −4.335 | −3.625 | −2.916 | −24.774 | −70.97 |
1:2 | −3.777 | −3.762 | −3.748 | −4.195 | −1.451 |
2:1 | −3.268 | −2.964 | −2.660 | −12.022 | −30.399 |
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Sun, X.; Lv, X.; Han, C.; Bai, L.; Wang, T.; Sun, Y. Fabrication of Polyethyleneimine-Modified Nanocellulose/Magnetic Bentonite Composite as a Functional Biosorbent for Efficient Removal of Cu(Ⅱ). Water 2022, 14, 2656. https://doi.org/10.3390/w14172656
Sun X, Lv X, Han C, Bai L, Wang T, Sun Y. Fabrication of Polyethyleneimine-Modified Nanocellulose/Magnetic Bentonite Composite as a Functional Biosorbent for Efficient Removal of Cu(Ⅱ). Water. 2022; 14(17):2656. https://doi.org/10.3390/w14172656
Chicago/Turabian StyleSun, Xiaoyin, Xintian Lv, Caohui Han, Lu Bai, Tingting Wang, and Yongchang Sun. 2022. "Fabrication of Polyethyleneimine-Modified Nanocellulose/Magnetic Bentonite Composite as a Functional Biosorbent for Efficient Removal of Cu(Ⅱ)" Water 14, no. 17: 2656. https://doi.org/10.3390/w14172656