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Hydrothermal carbonization and pyrolysis of sewage sludges: What happen to carbon and nitrogen?

机译:污水污泥的水热碳化和热解:碳和氮会发生什么?

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Hygienization by thermochemical carbonization may be one option to enable the use of sewage sludge (SS) as soil amendment and nitrogen (N) fertilizer. To evaluate this possibility, SS derived from different water purification processes of a rural waste water treatment plant were hydrothermal carbonized (HTC) at 200 and 260 degrees C for 0.5 and 3.0 h, and pyrolyzed at 600 degrees C for 1 h. During HTC, temperature rather than residence time affected the chemical alteration. Solid-state C-13 and N-15 nuclear magnetic resonance (NMR) spectroscopy showed considerably lower aromaticity in the hydrochars than in the pyrochars. Whereas the aromatic network of the hydrochars is dominated by polyfurans and N-heterocyclic aromatic units that of the pyrochars is mainly composed of arene structures. The highest total and inorganic N contents were obtained via HTC at 200 degrees C for 30 min, thus this material may be applied if both immediate and slow N release is needed.
机译:通过热化学碳化进行卫生处理可能是使污水污泥(SS)用作土壤改良剂和氮(N)肥料的一种选择。为了评估这种可能性,将来自农村污水处理厂不同净水工艺​​的SS分别在200和260摄氏度下进行0.5和3.0小时的水热碳化(HTC),然后在600摄氏度下进行热解1小时。在HTC期间,温度而不是停留时间会影响化学变化。固态C-13和N-15核磁共振(NMR)光谱显示,与焦炭相比,水炭中的芳香性低得多。而水煤的芳族网络主要由聚呋喃和N-杂环芳族单元组成,焦煤的芳族网络主要由芳烃结构组成。通过HTC在200摄氏度下30分钟可获得最高的总N和无机N含量,因此,如果需要立即释放N和缓慢释放N,则可以使用此材料。

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