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Mechanisms of Pb and/or Zn adsorption by different biochars: Biochar characteristics, stability, and binding energies

机译:不同生物炭对铅和/或锌的吸附机理:生物炭的特性,稳定性和结合能

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摘要

Biochar has been widely studied as an amendment for use in remediation of water and soil contaminated with heavy metals such as Pb~(2+) and Zn~(2+), but the effects of biochar characteristics, including stability, on the competitive adsorption of Pb~(2+) and Zn~(2+) by biochars from various sources are incompletely understood. In this work, biochars from three different feedstocks, including rice straw (RS), chicken manure (CM), and sewage sludge (SS), were prepared at two pyrolysis temperatures, 550 and 350 ℃, and tested to investigate the influence of their stabilities and other characteristics on their adsorption of Pb~(2+) and Zn~(2+) in both single- and binary-metal systems. RS biochar had the highest carbon and hydrogen contents, greatest number of functional groups (e.g., O—H and C=C/C=0), highest pH, most negative surface charge, and highest physical stability, and thus the highest adsorption capacity for Pb~(2+) and Zn~(2+). Pyrolysis at the higher temperature resulted in a slight decrease in aromatic functional groups on biochar surfaces but higher adsorption capacities for Pb~(2+) and Zn~(2+) due to the decreased biochar particle size and increased specific surface area. FTIR, XRD, and XPS analyses indicated that Pb~(2+) and Zn~(2+) were absorbed on the biochars primarily via chemical complexation with aromatic functional groups. Quantum chemistry calculations confirmed that these functional groups (e.g., -OH and-COOH) tended to bind more strongly with Pb~(2+) than with Zn~(2+) due to the former's lower binding energies, which also accounted for the notable decrease in adsorption of Zn~(2+) in the presence of Pb~(2+). In addition, compared to carboxyl groups, hy-droxyl groups had smaller binding energies and stronger metal complexation. These findings provide a theoretical basis for improved understanding of potential applications of biochars in environmental remediation.
机译:生物炭已被广泛研究作为修正物,用于修复被Pb〜(2+)和Zn〜(2+)等重金属污染的水和土壤,但是生物炭特性(包括稳定性)对竞争性吸附的影响各种来源的生物炭对Pb〜(2+)和Zn〜(2+)的影响尚不完全清楚。在这项工作中,分别在550和350℃的两种热解温度下制备了三种不同原料的生物炭,包括稻草(RS),鸡粪(CM)和污水污泥(SS),并对其进行了测试。在单金属和二元金属体系中吸附Pb〜(2+)和Zn〜(2+)的稳定性和其他特性。 RS生物炭具有最高的碳和氢含量,最多的官能团数量(例如,OH和C = C / C = 0),最高的pH,最大的负表面电荷和最高的物理稳定性,因此具有最高的吸附能力对于Pb〜(2+)和Zn〜(2+)。高温下的热解导致生物炭表面的芳香族官能团略有减少,但由于生物炭粒径的减小和比表面积的增加,对Pb〜(2+)和Zn〜(2+)的吸附能力更高。 FTIR,XRD和XPS分析表明Pb〜(2+)和Zn〜(2+)主要通过与芳香族官能团的化学络合被吸收到生物炭上。量子化学计算证实,这些官能团(例如,-OH和-COOH)与Pb〜(2+)的结合力比与Zn〜(2+)的结合力强,这是由于前者的结合能较低,这也说明了Pb〜(2+)存在下Zn〜(2+)的吸附显着降低。另外,与羧基相比,羟烷基具有更小的结合能和更强的金属络合性。这些发现为更好地理解生物炭在环境修复中的潜在应用提供了理论基础。

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