Pseudomonas stutzeri Immobilized Sawdust Biochar for Nickel Ion Removal
Abstract
:1. Introduction
2. Results
2.1. Biochar Yield
2.2. Immobilization and Selection of Biochar
2.3. Characterization of SDB and PSDB
2.4. Effect of Operating Conditions on Ni2+ Removal
2.4.1. Effect of Incubation Time
2.4.2. Effect of Initial pH on Ni2+ Removal
2.4.3. Effect of Temperature
2.4.4. Effect of PSDB Dosage
2.4.5. Effect of Initial Ni2+ Concentration
2.5. Adsorption Kinetics and Isotherm Study of PSDB
2.5.1. Adsorption Kinetics
2.5.2. Adsorption Isotherm
2.6. Ni2+ Removal by SDB, P. stutzeri, and PSDB at Optimized Operating Conditions
2.7. Reusability of Immobilized Cell
2.8. FTIR Analysis of PSDB after Ni Removal
3. Materials and Methods
3.1. Chemicals
3.2. Preparation of Biochar
3.3. Microbial Cell Immobilization
3.4. Selection of Biochar Based on Immobilization Potential
3.5. Characterization of SDB
3.6. Effect of Operating Conditions on Ni2+ Removal
3.7. Adsorption Kinetics and Isotherm Study
3.8. Ni2+ Removal by SDB, Pseudomonas stutzeri and PSDB at Optimized Operating Conditions
3.9. Experimental Design for the Reusability Study of Immobilized Cell
4. Conclusions
Supplementary Materials
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
References
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Surface Area (m2 g−1) SDB | Total Pore Volume (cm3 g−1) | Average Pore Size (nm) | |
---|---|---|---|
SDB | 195.68 | 0.99 | 1.01 |
PSDB | 3.19 | 0.14 | 0.5 |
Ba | Fe | Mg | Mn | Zn | K | Cu | Pb |
---|---|---|---|---|---|---|---|
2.21 | 673.97 | 61.41 | 8.69 | 11.57 | 12 | 40 | 2.7 |
Models | Model Parameter | PSDB |
---|---|---|
Kinetic model | ||
Pseudo-second order | Qe (mg g−1) | 32.59 |
K2 (g mg−1 h−1) | 0.015 | |
R2 | 0.99 | |
Isotherm model | ||
Langmuir | Qm (mg g−1) | 67.06 |
KL (L mg−1) | 0.08 | |
R2 | 0.99 |
Support Material | Microorganism | Initial Concentration of Ni2+ | Removal Efficiency | Time | Mechanism | Ref. |
---|---|---|---|---|---|---|
Loofa sponge | Chlorella sorokiniana | 200 mg L−1 | 60.38 mg g−1 | 15 min | Biosorption | [44] |
Alginate | Bacillus cereus | 50 mg L−1 | 54 mg g−1 | - | Adsorption | [45] |
Ca-alginate beads | Sargassum sp. | 7 mmol L−1 | 1.69 mmol g−1 | Adsorption | [46] | |
Rice bran | Rhizopus arrhizus | 100 mg L−1 | 6.83 mg g−1 | 90 min | Biosorption | [47] |
Polyacrylamide beads | Enterobacter species | 10 mg L−1 | 42% | 30 min | Accumulation | [48] |
Polyvinyl alcohol hydrogel | Aspergillus niger, strain B 77 | 0.9 mg L−1 | 48.9% | 5 min | Biosorption | [49] |
Ca-alginate | Aspergillus niger, strain | 0.9 mg L−1 | 54.4% | 5 min | Biosorption | [49] |
Peanut shell biochar | Pseudomonas hibiscicola strain L1 | 20 mg L−1 | 77.34% | 120 h | - | [43] |
Saw dust biochar | Pseudomonas stutzeri | 10 mg L−1 | 83% | 36 h | Adsorption Bioaccumulation | Present study |
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Manikandan, S.K.; Nair, V. Pseudomonas stutzeri Immobilized Sawdust Biochar for Nickel Ion Removal. Catalysts 2022, 12, 1495. https://doi.org/10.3390/catal12121495
Manikandan SK, Nair V. Pseudomonas stutzeri Immobilized Sawdust Biochar for Nickel Ion Removal. Catalysts. 2022; 12(12):1495. https://doi.org/10.3390/catal12121495
Chicago/Turabian StyleManikandan, Soumya Koippully, and Vaishakh Nair. 2022. "Pseudomonas stutzeri Immobilized Sawdust Biochar for Nickel Ion Removal" Catalysts 12, no. 12: 1495. https://doi.org/10.3390/catal12121495