2017
DOI: 10.1016/j.biortech.2017.06.084
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Challenges and recent advances in biochar as low-cost biosorbent: From batch assays to continuous-flow systems

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Cited by 220 publications
(78 citation statements)
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“…In the current study, we used Norway spruce biochar in the columns. The N adsorption capacity of the biochar reactor can be significantly affected by the biochar feedstock, treatment temperature, and initial concentration [57]. Under high initial N concentration, the adsorption capacity of wood biochars can reach up to 50-125 mg NH 4 N g −1 biochar and 2-8 mg NO 3 N g −1 biochar [46].…”
Section: Evaluation Of the Experimentsmentioning
confidence: 99%
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“…In the current study, we used Norway spruce biochar in the columns. The N adsorption capacity of the biochar reactor can be significantly affected by the biochar feedstock, treatment temperature, and initial concentration [57]. Under high initial N concentration, the adsorption capacity of wood biochars can reach up to 50-125 mg NH 4 N g −1 biochar and 2-8 mg NO 3 N g −1 biochar [46].…”
Section: Evaluation Of the Experimentsmentioning
confidence: 99%
“…Adsorption is the main process in the removal of N from water. In the adsorption, ion exchange and electrostatic adsorption occurs between surface functional groups and N fractions [57].…”
Section: Evaluation Of the Experimentsmentioning
confidence: 99%
“…Biochar obtained from the pyrolysis of woody biomass can be used for a number of purposes, such as for soil amendment [1][2][3][4], and as a low cost adsorbent [5][6][7][8][9][10]. As far as the former application is concerned, biochar has been demonstrated to improve soil properties [11][12][13][14][15][16][17], as well as to reduce contaminant leaching [18][19][20][21][22][23].…”
Section: Introductionmentioning
confidence: 99%
“…33,34 For example, the adsorption of hydrophobic organic contaminants (HOCs) on low-temperature biochars that generally contained more hydrophilic groups could be involved in more interactions via specic adsorption including Hbonding and p-p EDA interaction between the aromatic surfaces of carbonaceous adsorbent and adsorbate. 35 In contrast, these surface polar oxygen-containing functional groups were expected to form three-dimensional water clusters via strong H-bonding and then hinder HOCs from approaching the available adsorption sites, in turn, suppressing the adsorption of HOCs by biochars. 30 In addition, the surface polarity of biochar was also found to play an important role in controlling the adsorption of organic contaminants by p-p EDA interactions between electron-rich (p-donor) and p-acceptor sites in organic matter within the biochar.…”
Section: Structure-activity Relationship Between Biochar Physicochemimentioning
confidence: 99%