High-Performance Materials from Bio-based Feedstocks. Группа авторов

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A degradation through activation of peroxymonosulfate. Journal of Hazardous Materials 388: 121801. https://doi.org/10.1016/j.jhazmat.2019.121801.

      144 144. Wataniyakul, P., Boonnoun, P., Quitain, A.T. et al. (2018). Preparation of hydrothermal carbon acid catalyst from defatted rice bran. Industrial Crops and Products 117: 286–294. https://doi.org/10.1016/j.indcrop.2018.03.002.

      145 145. Ibrahim, S.F., Asikin‐Mijan, N., Ibrahim, M.L. et al. (2020). Sulfonated functionalization of carbon derived corncob residue via hydrothermal synthesis route for esterification of palm fatty acid distillate. Energy Conversion and Management 210: 112698. https://doi.org/10.1016/j.enconman.2020.112698.

      146 146. Yamaguchi, D., Kitano, M., Suganuma, S. et al. (2009). Hydrolysis of cellulose by a solid acid catalyst under optimal reaction conditions. Journal of Physical Chemistry C 113 (8): 3181–3188. https://doi.org/10.1021/jp808676d.

      147 147. Zong, M.H., Duan, Z.Q., Lou, W.Y. et al. (2007). Preparation of a sugar catalyst and its use for highly efficient production of biodiesel. Green Chemistry 9 (5): 434–437. https://doi.org/10.1039/b615447f.

      148 148. Yao, Y., Lian, C., Wu, G. et al. (2017). Synthesis of “sea urchin”‐like carbon nanotubes/porous carbon superstructures derived from waste biomass for treatment of various contaminants. Applied Catalysis B: Environmental 219: 563–571. https://doi.org/10.1016/j.apcatb.2017.07.064.

      149 149. Ming, J., Liu, R., Liang, G. et al. (2011). Knitting an oxygenated network‐coat on carbon nanotubes from biomass and their applications in catalysis. Journal of Materials Chemistry 21 (29): 10929–10934. https://doi.org/10.1039/c1jm10989h.

      150 150. Das, V.K., Shifrina, Z.B., and Bronstein, L.M. (2017). Graphene and graphene‐like materials in biomass conversion: paving the way to the future. Journal of Materials Chemistry A 5 (48): 25131–25143. https://doi.org/10.1039/c7ta09418c.

      151 151. Jurca, B., Bucur, C., Primo, A. et al. (2019). N‐Doped defective graphene from biomass as catalyst for CO2 hydrogenation to methane. ChemCatChem 11 (3): 985–990. https://doi.org/10.1002/cctc.201801984.

      152 152. Huang, B., Xia, M., Qiu, J. et al. (2019). Biomass derived graphene‐like carbons for electrocatalytic oxygen reduction reaction. ChemNanoMat 5 (5): 682–689. https://doi.org/10.1002/cnma.201900009.

      153 153. Wu, L., Song, J., Zhou, B. et al. (2016). Preparation of Ru/graphene using glucose as carbon source and hydrogenation of levulinic acid to γ‐valerolactone. Chemistry – An Asian Journal 11 (19): 2792–2796. https://doi.org/10.1002/asia.201600453.

       Duncan J. Macquarrie, Tabitha H.M. Petchey and Cinthia J. Meña Duran

       Green Chemistry Centre of Excellence, Department of Chemistry, University of York, York, UK

      Porous materials are of great importance in a wide range of applications, including adsorption, catalysis, energy applications and composite materials. The majority of these materials are microporous; from the International Union of Pure and Applied Chemistry(IUPAC) definition [1, 2] they contain pores of <2 nm. In reality, the pores are generally constrained to <1 nm, making them able to adsorb small molecules within their pore structure, whereas larger molecules can only adsorb externally, meaning that the majority of the surface area is unavailable. Long micropores also suffer from diffusional issues, and it is recognised that much of a pore system may indeed play little role in the material’s performance.

      While (amorphous unstructured) mesoporous materials such as silica and alumina have been known for decades, more regular materials took much longer to develop. It was the early 1990s that saw an explosion of methodologies that delivered a wide range of very controllable routes to highly regular structured materials, largely silicas, but also a few alumina systems and others were developed [3, 4]. This work served to illustrate the advantages of mesoporosity, with a range of applications being demonstrated.

      While these strides were being made in inorganic materials, the field of carbon was still dominated by predominantly microporous activated carbons, generally prepared in two steps. The first step is the thermal decomposition of waste biomass, which is followed by a chemical ‘activation’ step. This second step usually involved reaction with metal species (KOH and ZnCl2 in large quantities) or gases (oxidants such as oxygen or CO2) in order to open up the structure and generate some mesoporosity. Nonetheless, these materials remain predominantly microporous.

      The enormous activity in well‐defined, highly mesoporous inorganic materials led to their use as templates, including for carbon, and various groups have published work showing that the mesopores could be filled with organic material which could then be carbonised [5, 6]. Removal of the inorganic template then gave an inverse replica carbonaceous material that often displayed mesoporosity.

      These so‐called hard templating methods provide a wide range of well‐ordered materials [7] but have the drawback of complex and wasteful syntheses, destroying both the template for the silica and the silica itself. An elegant approach has recently been put forward by Jiang et al. [8] who coated the internal surface of mesoporous silicas with a layer of carbon, leading to carbon silica composites (CSCs). Such CSCs directly replicate the porosity of the silica but have a carbonaceous surface. This route is simpler, less wasteful, and retains positive features from the silica, including mechanical strength and the variety of pore architectures that silica can have.

      Another approach, first published in 2006, utilises the inherent structure of certain polysaccharides to expand to give mesostructured hydrogels [9]. With suitable drying strategies, these gels can be dried and the resultant aerogel is pyrolysed to provide a highly mesoporous material with excellent pore volume, surface area, and importantly, tunable surface properties ranging from polysaccharide‐like at lower pyrolysis temperatures to carbon‐like at higher temperatures. While the process consists of three stages, it does not involve templating, instead relying on the inherent properties of the starch to assemble into naturally mesoporous structures. These materials are known as Starbon®, from a combination of starch and carbon, and will be the focus of this chapter. Starbon has been commercialised by Starbons

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