Abstract:Biomass is a green energy source and is available in abundance. Biochar is a carbon-rich material derived from a wide range of biomass or organic waste through the thermochemical route. Biochar has received increasing attention because of its distinctive properties such as high carbon content, greater specific surface area, cation exchange capacity, nutrient retention capacity, and stable structure. This review paper extensively studies and reports the different pyrolysis processes, reactor types, the effect o… Show more
“…The aim of the second step—CO 2 activation at 850°C was to develop a microporous structure which—as we anticipated—will play a crucial role in the adsorption experiments. Generally, the treatment's conditions were selected to be typical for biomass pyrolysis (oxygen‐free environment, temperature range of 300–500°C) and activation (CO 2 flow, temperature range of 700–900°C; Reza et al, 2020; Sakhiya et al, 2020). The physical processes and chemical reactions that occur during pyrolysis are complex and depend both, on the source of the biomass and the processing parameters.…”
Residues obtained after wood biomass liquefaction were used as precursors for the synthesis of two activated biochars. The source of biomass liquefaction constituted of industrial wood processing by‐products, including bark and wood sawdust. The liquefied residues were analyzed in terms of chemical components and structure. Carbonization under nitrogen atmosphere followed by physical CO2 activation allowed to obtain microporous activated carbons with specific surface areas of 741 and 522 m2 g−1, and micropore volumes of 0.38 and 0.27 cm3 g−1, respectively. The obtained activated carbons were used to remove toxic hexavalent chromium from the aquatic environment. The observed sorption capacities were 80.6 mg g−1 versus 36.7 mg g−1 for wood bark‐derived and wood sawdust‐derived carbon, respectively, indicating a key role of the wood residue source in the effectiveness of Cr(VI) removal by resulting carbons. Despite the dominant microporous structure, the adsorption kinetics was surprisingly fast, especially for the bark‐derived carbon, since the adsorption equilibrium was reached within 2 h. The sorption mechanism of chromium was based on the carbon surface‐mediated reduction of toxic hexavalent form to its non‐toxic trivalent form, as confirmed by the X‐ray photoelectron analysis. Therefore, the residues from wood liquefaction can be easily converted into porous activated biocarbons capable of adsorbing significant amounts of hazardous Cr(VI) while reducing them to non‐toxic Cr(III).
“…The aim of the second step—CO 2 activation at 850°C was to develop a microporous structure which—as we anticipated—will play a crucial role in the adsorption experiments. Generally, the treatment's conditions were selected to be typical for biomass pyrolysis (oxygen‐free environment, temperature range of 300–500°C) and activation (CO 2 flow, temperature range of 700–900°C; Reza et al, 2020; Sakhiya et al, 2020). The physical processes and chemical reactions that occur during pyrolysis are complex and depend both, on the source of the biomass and the processing parameters.…”
Residues obtained after wood biomass liquefaction were used as precursors for the synthesis of two activated biochars. The source of biomass liquefaction constituted of industrial wood processing by‐products, including bark and wood sawdust. The liquefied residues were analyzed in terms of chemical components and structure. Carbonization under nitrogen atmosphere followed by physical CO2 activation allowed to obtain microporous activated carbons with specific surface areas of 741 and 522 m2 g−1, and micropore volumes of 0.38 and 0.27 cm3 g−1, respectively. The obtained activated carbons were used to remove toxic hexavalent chromium from the aquatic environment. The observed sorption capacities were 80.6 mg g−1 versus 36.7 mg g−1 for wood bark‐derived and wood sawdust‐derived carbon, respectively, indicating a key role of the wood residue source in the effectiveness of Cr(VI) removal by resulting carbons. Despite the dominant microporous structure, the adsorption kinetics was surprisingly fast, especially for the bark‐derived carbon, since the adsorption equilibrium was reached within 2 h. The sorption mechanism of chromium was based on the carbon surface‐mediated reduction of toxic hexavalent form to its non‐toxic trivalent form, as confirmed by the X‐ray photoelectron analysis. Therefore, the residues from wood liquefaction can be easily converted into porous activated biocarbons capable of adsorbing significant amounts of hazardous Cr(VI) while reducing them to non‐toxic Cr(III).
“…Biochar's preparation condition also influence its physicochemical properties, which indirectly also control its HM immobilisation effects (Wang et al 2021). The production parameters that were found to control these biochar properties include, pyrolysis temperature, heating rates, vapour residence time, biomass type and particle size (Sakhiya et al 2020). Hence, recent biochar research directed at HM remediation highlights routes to improvement and modification of biochar's HM absorption efficacy through altering its production processes (Wang et al 2019).…”
Section: Improvement Of Biochar's Efficacy For Heavy Metal Remediationmentioning
confidence: 99%
“…Gas purging of biochar (another physical modification process) with CO 2 at high temperature was found to increase biochar surface area and pore volume relative to unmodified ones (Xiong et al 2013). Chemical modification, in general, is a heat treatment process (450-900 °C) of biochar with chemical activating reagents (Sakhiya et al 2020). Studies show that chemical modification creates opportunities for biochar to chemically react with HMs more efficiently through (1) increased surface area and sorption sites; (2) more conducive surface to electrostatic attraction, surface complexation, and/or precipitation, and (3) specific surface functional groups for greater sorption affinity and stronger interactions (Rajapaksha et al 2016).…”
The focus of this study is on the soil physicochemical, biological, and microbiological processes altered by biochar application to heavy metal (HM) contaminated soils. The aim is to highlight agronomical and environmental issues by which the restorative capacity of biochar might be developed. Literature shows biochar can induce soil remediation, however, it is unclear how soil processes are linked mechanistically to biochar production and if these processes can be manipulated to enhance soil remediation. The literature often fails to contribute to an improved understanding of the mechanisms by which biochar alters soil function. It is clear that factors such as biochar feedstock, pyrolysis conditions, application rate, and soil type are determinants in biochar soil functionality. These factors are developed to enhance our insight into production routes and the benefits of biochar in HM soil remediation. Despite a large number of studies of biochar in soils, there is little understanding of long-term effects, this is particularly true with respect to the use and need for reapplication in soil remediation.
“…At elevated temperature, those materials are broken down in simple compounds and this process is known as thermochemical depolymerization reactions. The thermochemical decomposition "pyrolysis" of biomass, generally, takes place in an oxygen-free environment within a temperature range of 300-500 °C to produce the char (Sakhiya, Anand and Kaushal, 2020). This bio decomposition process converts low-energy-density biomass into a high-density liquid product called "bio-oil", medium caloric value gas called "synthesis gas", and high-density solid product called "biochar".…”
Section: Biocharmentioning
confidence: 99%
“…The activation here means a technique applied physically or chemically to biochar to improve its physical characteristics (i.e. specific surface area) and absorption capacity (Sakhiya, Anand and Kaushal, 2020). The activated biochar serves multiple purposes like soil amendment in agriculture, absorbent of contaminant and pollutant in aqueous solutions; it can be used also as catalysts of chemical reactions, fuel alternative, used as an additive, used in the construction sector.…”
The study was carried out to identify potential value addition to tomato crop farm-leftovers and investigate their existing end-uses to suggest a collaboration model between tomato farmers in Nkotsi Sector and IPRC Musanze. The findings confirmed that the tomato crop stems are the main type of tomato crop farm-leftovers found on the farm, leaves and roots are also present in minor quantities. Those farm-leftovers are mainly used for compost making, some remain unused at farm level, and few are used for feeding animals. For whatever destination, the tomato crop farm-leftovers do not generate any cash to farmers, and unfortunately, 91% of farmers are not aware of crop farm-leftovers negative effects. All respondents know the IPRC Musanze, and 59% of them recognize its community outreach activities. However, 97% of farmers do not have any previous collaboration with the college even though they show willingness for future collaboration. 62% of interviewed IPRC Musanze TVET trainers revealed limited advanced tomatoes farming activities in the area, and crop farm-leftovers negative effects. A collaboration model between farmers and the college is designed as a new way of working to boost tomato farming in the area as well as improving the quality of TVET training offered by the college. The stable relations, trust, shared problem, resources, planned joint activities and their execution are the elements of the proposed model. Therefore, technical training, joint applied research and innovation activities, joint problem-solving initiatives were suggested as the starting point for the proposed model.
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