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将生产乙酰丙酸后回收的水凝胶转化为活性炭吸附剂。

Conversion of the hydrochar recovered after levulinic acid production into activated carbon adsorbents.

机构信息

Dipartimento di Chimica e Chimica Industriale - Università di Pisa, Via Giuseppe Moruzzi 13, 56124 Pisa, Italy; Consorzio Interuniversitario Reattività Chimica e Catalisi (CIRCC), Via Celso Ulpiani 27, 70126 Bari, Italy.

Dipartimento di Chimica e Chimica Industriale - Università di Pisa, Via Giuseppe Moruzzi 13, 56124 Pisa, Italy; Consorzio Interuniversitario Reattività Chimica e Catalisi (CIRCC), Via Celso Ulpiani 27, 70126 Bari, Italy.

出版信息

Waste Manag. 2023 Aug 1;168:235-245. doi: 10.1016/j.wasman.2023.06.012. Epub 2023 Jun 13.

DOI:10.1016/j.wasman.2023.06.012
PMID:37320891
Abstract

Levulinic acid production by acid-catalyzed hydrothermal conversion of (ligno)cellulosic biomass generates significant amounts of carbonaceous hydrochar, which is currently considered a final waste. In this work, the hydrochar recovered after the levulinic acid production, was subjected to cascade pyrolysis and chemical activation treatments (by HPO or KOH), to synthesize activated carbons. The pyrolysis post-treatment was already effective in improving the surface properties of the raw hydrochar (Specific Surface Area: 388 m/g, V: 0.22 cm/g, V: 0.07 cm/g, V: 0.14 cm/g), by removing volatile compounds. KOH activation resulted as the most appropriate for further improving the surface properties of the pyrolyzed hydrochar, showing the best surface properties (Specific Surface Area: 1421 m/g, V: 0.63 cm/g, V: 0.10 cm/g, V: 0.52 cm/g), which synergistically makes it a promising system towards adsorption of CO (∼90 mg/g) and methylene blue (∼248 mg/g). In addition, promising surface properties can be achieved after direct chemical activation of the raw hazelnut shells, preferably by HPO (Specific Surface Area: 1918 m/g, V: 1.34 cm/g, V: 0.82 cm/g, V: 0.50 cm/g), but this choice is not the smartest, as it does not allow the valorization of the cellulose fraction to levulinic acid. Our approach paves the way for possible uses of these hydrochars originating from the levulinic acid chain for new environmental applications, thus smartly closing the biorefinery loop of the hazelnut shells.

摘要

酸催化水热转化(木质)纤维素生物质生产乙酰丙酸会产生大量的碳质水热炭,目前被认为是最终废物。在这项工作中,从乙酰丙酸生产中回收的水热炭经过级联热解和化学活化处理(用 HPO 或 KOH),合成了活性炭。热解后处理已经有效地改善了原始水热炭的表面性质(比表面积:388 m/g,V:0.22 cm/g,V:0.07 cm/g,V:0.14 cm/g),通过去除挥发性化合物。KOH 活化是进一步改善热解水热炭表面性质的最适宜方法,显示出最好的表面性质(比表面积:1421 m/g,V:0.63 cm/g,V:0.10 cm/g,V:0.52 cm/g),协同作用使其成为 CO(约 90 mg/g)和亚甲基蓝(约 248 mg/g)吸附的有前途的体系。此外,通过直接用 HPO 对榛子壳进行化学活化(比表面积:1918 m/g,V:1.34 cm/g,V:0.82 cm/g,V:0.50 cm/g),可以获得有前途的表面性质,但这不是最明智的选择,因为它不能将纤维素部分转化为乙酰丙酸。我们的方法为这些源自乙酰丙酸链的水热炭在新的环境应用中的可能用途铺平了道路,从而巧妙地关闭了榛子壳的生物炼制循环。

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