Table 17.
Raw feedstock | Temperature | Production pathway | Target contaminant | Maximum adsorption capacity (mg g−1) | Adsorption mechanism | References |
---|---|---|---|---|---|---|
Orange peel waste | 150–600 °C | Microwave pyrolysis via carbon dioxide and steam activation | Congo red | 136.00 | Electrostatic interaction | Yek et al. (2020) |
Hickory chips | 600 °C | Pyrolysis followed by impregnation with iron (II, III) oxide | Methylene blue | 500.5 | Electrostatic interaction and π–π interaction | Li et al. (2020e) |
Switchgrass | 900 °C | Pyrolysis | Orange G | 38.2 | Electrostatic interaction, and π–π interaction | Park et al. (2019) |
Frass of mealworms | 800 °C | Pyrolysis | Malachite green | 1738.6 | Electrostatic interaction, hydrogen bonding, and π–π interaction | Yang et al. (2019b) |
Corncob | 400 °C | Pyrolysis followed by impregnation with triethylenetetramine, and treatment with sulphuric acid | Sunset yellow | 77.1 | Electrostatic interaction | Mahmoud et al. (2020) |
Macroalgae (Undaria pinnatifida) | 800 °C | Chemical functionalisation with potassium hydroxide followed by pyrolysis | Rhodamine B | 533.8 | Electrostatic interaction, hydrogen bonding, van der Waals forces, and π–π interaction | Yao et al. (2020) |
Methylene blue | 841.64 | |||||
Malachite green | 4066.96 | |||||
Corn straw | 500 °C | Nitric acid treatment, sodium hydroxide activation, followed by pyrolysis iron (III) chloride modification | Malachite green | 515.8 | Electrostatic attraction | Eltaweil et al. (2020) |
Swine manure and fly ash | 700 °C | Pretreatment of fly ash with sodium hydroxide, mixing with swine manure and pyrolysis | Methylene blue | 131.6 | Electrostatic interaction, and π–π interaction | Wang et al. (2020c) |
Tapioca peel waste | 800 °C | Mixing of pyrolysed feedstock with thiourea and pyrolysis | Rhodamine B | 33.1 | Electrostatic interaction, and Hydrogen bonding | Vigneshwaran et al. (2021) |
Malachite Green | 30.18 | |||||
Switchgrass | 900 °C | Pyrolysis | Congo red | 22.6 | Electrostatic interaction, and π–π interaction | Park et al. (2019) |
Wakame (macroalgae) | 800 °C | Chemical functionalisation with potassium hydroxide followed by pyrolysis | Malachite green | 4066.9 | Electrostatic interaction, π–π stacking, hydrogen bonding, and van der Waals force | Yao et al. (2020) |
Rice straw | 500 °C | Pyrolysis followed by wet attrition | Methylene blue | 90.91 | Electrostatic interaction | Abd-Elhamid et al. (2020) |
Crystal violet | 44.64 | |||||
Corncob | 400 °C | Pyrolysis followed by partial oxidation and amination | Congo red | 89.3 | Chemisorption | Faheem et al. (2019) |
Chicken manure | 500 °C | Pyrolysis | Phenols | 106.2 | Electrostatic interaction, π–π interaction, and hydrogen bonding | Thang et al. (2019) |
2,4-dinitrophenol | 148.1 | |||||
Alfalfa | 700 °C | Pyrolysis followed by nitric acid treatment, acid pickling, and reheating | p-Nitrophenol | 49.25 | Hydrogen bonding, and π–π interaction | Chen et al. (2019) |
Malt bagasse | 500–900 °C | Pyrolysis followed by zinc chloride activation; pyrolysis followed by hydrochloric acid treatment | 2-chlorophenol | 150.0 | Electrostatic interaction | Machado et al. (2020) |
Alfalfa | 650 °C | Pyrolysis | Bisphenol A | 63.0 | π–π interaction, and hydrophobic interaction | Choi and Kan (2019) |
Rice husk | 450 °C | Pyrolysis followed by potassium hydroxide functionalisation | Phenols | 179.0 | π–π interaction, and hydrogen bonding | Shen et al. (2020) |
Furniture waste | 700 °C | Pyrolysis followed by coating with fulvic acid | 4-chlorophenol | 133.0 | Hydrogen bonding, and π–π interaction | Wu and Chen (2019) |
Macroalgae | 800 °C | Pyrolysis followed by hydrochloric acid treatment | Pyrene | 0.19 | Hydrophobic interaction | Qiao et al. (2018) |
Corn straw | 500–800 °C | Pyrolysis followed by mixing with potassium hydroxide, and then pyrolysis | Naphthalene | 450.4 | π–π interaction, and pore filling | Qu et al. (2021) |
Rice husk | 500 °C | Pyrolysis followed by iron (II) sulphate modification | Phenanthrene | 97.6 | π–π interaction, hydrophobic interactions, and pore filling | Guo et al. (2018a) |
Macroalgae | 800 °C | Zinc chloride and iron (III) chloride modification, followed by pyrolysis, and hydrochloric acid treatment | Naphthalene | 90.0 | π–π interaction, partitioning effect, and pore filling | Cheng et al. (2020b) |
Alfalfa | 650 °C | Pyrolysis | Sulphamethoxazole | 90.0 | π–π interaction, and hydrophobic interactions | Choi and Kan (2019) |
Rice straw | 550 °C | Pyrolysis followed by hydrochloric acid treatment | Benzoic acid | 7.97 | π–π interaction, and van der Waals attractions | Singh et al. (2020) |
Microalgae | 750 °C | Pyrolysis | Tetracycline | 132.8 | Hydrophobic interactions, and π–π interaction | Choi et al. (2020) |
Grape pomace | 350 °C | Pyrolysis | Cymoxanil pesticide | 161.0 | Hydrophilic interactions | Yoon et al. (2021) |
Corn cob | 600 °C | Pyrolysis followed by hydrofluoric acid treatment | 2,4-dichlorophenoxyaceti acid (2,4-D) herbicide | 34.4 | Hydrogen bonding, pore filling, and π–π interaction | Binh and Nguyen (2020) |
Lotus seedpod | 500–650 °C | Pyrolysis followed by potassium hydroxide activation and pyrolysis | 17β-estradiol hormone | 183.6 | π–π interaction, and electrostatic interaction | Liu et al. (2020b) |
Different biomass-based feedstocks were studied against the targeted contaminants. Pre- or post-treatments were also investigated along with the temperatures at which the biochar was prepared. The maximum adsorption capacity in mg g−1 along with the adsorption mechanism are provided