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生物炭-水界面的金属相互作用:流动吸附微量热法阐明的能量学和结构-吸附关系。

Metal interactions at the biochar-water interface: energetics and structure-sorption relationships elucidated by flow adsorption microcalorimetry.

机构信息

Water Management and Hydrologic Sciences, Texas A & M University, College Station, Texas 77843, United States.

出版信息

Environ Sci Technol. 2011 Jul 1;45(13):5550-6. doi: 10.1021/es104401h. Epub 2011 Jun 1.

Abstract

Plant-derived biochars exhibit large physicochemical heterogeneity due to variations in biomass chemistry and combustion conditions. However, the influence of biochar heterogeneity on biochar-metal interaction mechanisms has not been systematically described. We used flow adsorption microcalorimetry to study structure-sorption relationships between twelve plant-derived biochars and two metals (K(+) and Cd(2+)) of different Lewis acidity. Irrespective of the biochar structure, sorption of K(+) (a hard Lewis acid) occurred predominantly on deprotonated functional groups via ion exchange with molar heats of adsorption (ΔH(ads)) of -4 kJ mol(-1) to -8 kJ mol(-1). By comparison, although ion exchange could not be completely ruled out, our data pointed to Cd(2+) (a soft Lewis acid) sorption occurring predominantly via two distinct cation-π bonding mechanisms, each with ΔH(ads) of +17 kJ mol(-1). The first, evident in low charge-low carbonized biochars, suggested Cd(2+)-π bonding to soft ligands such as -C ═ O; while the second, evident in low charge-highly carbonized biochars, pointed to Cd(2+)-π bonding with electron-rich domains on aromatic structures. Quantitative contributions of these mechanisms to Cd(2+) sorption can exceed 3 times that expected for ion exchange and therefore could have significant implications for the biogeochemical cycling of metals in fire-impacted or biochar-amended systems.

摘要

由于生物质化学组成和燃烧条件的变化,植物源生物炭表现出较大的物理化学异质性。然而,生物炭的异质性对生物炭-金属相互作用机制的影响尚未得到系统的描述。我们使用流动吸附微量热法研究了十二种植物源生物炭与两种金属(K(+)和 Cd(2+))之间的结构-吸附关系,这两种金属的路易斯酸度不同。无论生物炭的结构如何,K(+)(硬路易斯酸)的吸附主要通过与摩尔吸附热(ΔH(ads))为-4 kJ mol(-1)至-8 kJ mol(-1)的去质子化官能团进行离子交换来发生。相比之下,尽管不能完全排除离子交换的可能性,但我们的数据表明 Cd(2+)(软路易斯酸)的吸附主要通过两种不同的阳离子-π键合机制发生,每种机制的吸附热(ΔH(ads))为+17 kJ mol(-1)。第一种机制在低电荷低碳化生物炭中明显,表明 Cd(2+)-π 键合到软配体如 -C ═ O;而第二种机制在低电荷高碳化生物炭中明显,表明 Cd(2+)-π 键合到芳构结构上的富电子区域。这些机制对 Cd(2+)吸附的定量贡献可以超过离子交换预期值的 3 倍,因此可能对火灾影响或生物炭改良系统中金属的生物地球化学循环有重要意义。

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