杂草生物炭的开发及生物炭性能与重金属脱除能力的关系

V. Parcha, Amita Sati, Pankaj Bhandari
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引用次数: 0

摘要

生物炭是富碳生物质(<700℃)在限氧环境下热降解产生的热原黑炭,通常具有多孔结构,表面富含含氧官能团,吸附能力强,具有一定的表面积和稳定性。生物炭有多种用途,包括用于土壤修复和水和土壤污染控制的农业应用。生物炭具有几个显著的社会经济和环境效益,如固碳、去除污染物和改善土壤。热解温度影响生物炭的性质,进而决定其应用潜力。收集的克罗夫顿杂草(除了根)被清洗,在室温下风干,并粉碎通过一个10目的筛子。在这里,我们研究了在300°C、400°C、500°C和600°C不同热解温度下产生的Crofton weed生物炭(C- bc)的特性。我们测量了产率、灰分含量、pH值、碘吸附值(ISV)和C-BC的元素组成。我们还使用扫描电子显微镜(SEM)表征了C-BC,以及它从水溶液中去除Pb2+和Cd2+污染物的能力。C- BC产率随热解温度升高而降低,而灰分含量和pH值升高。ISV在300-400°C时首先升高,在500-600°C时下降。300 ~ 600℃热解生成的C- bc(分别为C- bc300 ~ C- bc600), H、N、O含量随温度升高而降低,C、Ca、Mg、P、K含量随温度升高而升高。所有的c - bc都具有一定数量的孔隙结构。热解温度的升高降低了C-BC表面-OH、-COOH、脂肪族C-H和极性C-O的含量。随着热解温度的升高,Pb2+和Cd2+的去除率增加。总体而言,对于C-BC,低热解温度有利于制备多孔性更强的生物炭,水溶性钙、镁、氮、磷含量增加,而高热解温度制备的生物炭具有较高的碱度、芳香性和稳定性,以及重金属去除活性
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Development of biochar from crofton weed & relationship between biochar properties and its applicability as a heavy metal removal activity
Biochar is a pyrogenic black carbon produced from thermal degradation of carbon-rich biomass (<700°C) in an oxygen-limited environment, and usually has a porous structure, a surface rich in oxygenated functional groups, strong adsorption capacity, and a certain degree of surface area and stability. Biochar has multiple uses, including agricultural applications for soil remediation and pollution control in water and soil. Biochar has several significant socioeconomic and environmental benefits such as carbon sequestration, pollutant removal, and soil improvement. Pyrolysis temperature affects biochar properties, which in turn determines its application potential. The collected Crofton weed (except for the roots) was washed, air-dried at room temperature, and crushed for passage through a 10-mesh sieve. Here, we examined the properties of Crofton weed biochar (C-BC) produced at different pyrolysis temperatures of 300°C, 400°C, 500°C, and 600°C. We measured the yield, ash content, pH, iodine sorption value (ISV), and elemental composition of C-BC. We also characterized C-BC using scanning electron microscopy (SEM), as well as its ability to remove Pb2+and Cd2+contaminantsfrom an aqueous solution. C- BC yield decreased with increasing pyrolysis temperature, whereas ash content and pH increased. ISV first increased at 300–400°C and decreased at 500–600°C. For C-BC produced at pyrolysis temperatures 300–600°C (C-BC300 to C-BC600, respectively), H, N, and O content decreased, but C, Ca, Mg, P, and K content in- creased with increasing temperature. All C-BCs had a certain number of pore structures. Increasing pyrolysis temperatures decreased the amount of -OH, -COOH, aliphatic C-H, and polar C-O on the C-BC surface. The percentage of Pb2+and Cd2+removed increased with increasing pyrolysis temperatures. Overall, for C-BC, a low pyrolysis temperature was beneficial for producing a more porous biochar and increased content of water-soluble calcium, magnesium, nitrogen, and phosphorus, whereas high pyrolysis temperatures yield biochar that had high alkalinity, aromaticity, and stability, as well as heavy metal removal activity
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