2020
DOI: 10.1039/d0ra02038a
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Biochar prepared from maize straw and molasses fermentation wastewater: application for soil improvement

Abstract: A novel method was applied to improve biochar properties and its soil application by introducing molasses fermentation wastewater into a maize straw pyrolysis process.

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Cited by 8 publications
(5 citation statements)
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References 57 publications
(71 reference statements)
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“…Additionally, application of biochar materials in farmlands or contaminated sites releases large quantities of micro- and nanosized biochar particles, a significant portion of which may enter the atmospheric environment as dusts. , Accordingly, the abundance of FBPs in the environment is much higher than that of engineered nanoparticles . FBPs can actively participate in atmospheric photochemical reactions, resulting in the formation of atmospheric aerosols, and can pose ecotoxicological and human respiratory risks. , Owing to their large surface area, porous structures, aromaticity, and surface oxygen-functionality, FBPs can accumulate various organic contaminants ( e.g ., polycyclic aromatic hydrocarbons (PAHs) and heavy metals), either during pyrolysis or in the environment ( e.g ., through adsorption of contaminants from the aqueous solutions). Accordingly, the toxicological effects of contaminant-bearing FBPs should be attributed to the combined effects of both FBPs and the contaminants associated with these particles.…”
mentioning
confidence: 99%
“…Additionally, application of biochar materials in farmlands or contaminated sites releases large quantities of micro- and nanosized biochar particles, a significant portion of which may enter the atmospheric environment as dusts. , Accordingly, the abundance of FBPs in the environment is much higher than that of engineered nanoparticles . FBPs can actively participate in atmospheric photochemical reactions, resulting in the formation of atmospheric aerosols, and can pose ecotoxicological and human respiratory risks. , Owing to their large surface area, porous structures, aromaticity, and surface oxygen-functionality, FBPs can accumulate various organic contaminants ( e.g ., polycyclic aromatic hydrocarbons (PAHs) and heavy metals), either during pyrolysis or in the environment ( e.g ., through adsorption of contaminants from the aqueous solutions). Accordingly, the toxicological effects of contaminant-bearing FBPs should be attributed to the combined effects of both FBPs and the contaminants associated with these particles.…”
mentioning
confidence: 99%
“…According to the infrared spectra of CsBC300 and CsBC600 ( Fig. 2 ), both biochars contained different functional groups, like stretching vibration with a broad hydroxyl peak around 3400 cm −1 [ 32 , 33 ]. The stretching vibration peak of aliphatic CH2 was around 2925 cm −1 [ 34 , 35 ].…”
Section: Resultsmentioning
confidence: 99%
“…The specific surface area of biochar, in sandy soils, can also somewhat provide cation exchange capacity (Zhou et al, 2020), which is highly dependent on chemically reactive sites. These sites, in biochar, are formed over the years as the particles are attacked by microorganisms in the soil, changing the chemical and physical characteristics of the surface (Cohen-Ofri et al, 2006).…”
Section: Resultsmentioning
confidence: 99%