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模拟三氯乙烯在来源于大豆秸秆和花生壳废弃物的生物炭上的吸附动力学。

Modeling adsorption kinetics of trichloroethylene onto biochars derived from soybean stover and peanut shell wastes.

机构信息

Korea Biochar Research Center & Department of Biological Environment, Kangwon National University, Chuncheon, 200-701, South Korea.

出版信息

Environ Sci Pollut Res Int. 2013 Dec;20(12):8364-73. doi: 10.1007/s11356-013-1676-z. Epub 2013 Apr 23.

DOI:10.1007/s11356-013-1676-z
PMID:23608978
Abstract

Trichloroethylene (TCE) is one of the most hazardous organic pollutants in groundwater. Biochar produced from agricultural waste materials could serve as a novel carbonaceous adsorbent for removing organic contaminants from aqueous media. Biochars derived from pyrolysis of soybean stover at 300 °C and 700 °C (S-300 and S-700, respectively), and peanut shells at 300 °C and 700 °C (P-300 and P-700, respectively) were utilized as carbonaceous adsorbents to study batch aqueous TCE remediation kinetics. Different rate-based and diffusion-based kinetic models were adopted to understand the TCE adsorption mechanism on biochars. With an equilibrium time of 8-10 h, up to 69 % TCE was removed from water. Biochars produced at 700 °C were more effective than those produced at 300 °C. The P-700 and S-700 had lower molar H/C and O/C versus P-300 and S-300 resulting in high aromaticity and low polarity accompanying with high surface area and high adsorption capacity. The pseudo-second order and intraparticle diffusion models were well fitted to the kinetic data, thereby, indicating that chemisorption and pore diffusion were the dominating mechanisms of TCE adsorption onto biochars.

摘要

三氯乙烯(TCE)是地下水中最危险的有机污染物之一。由农业废料制成的生物炭可以作为一种新型的碳质吸附剂,用于从水介质中去除有机污染物。分别在 300°C 和 700°C(分别为 S-300 和 S-700)下由大豆秸秆和 300°C 和 700°C(分别为 P-300 和 P-700)下由花生壳热解得到的生物炭被用作碳质吸附剂,以研究批处理水相中 TCE 的修复动力学。采用了不同的基于速率和基于扩散的动力学模型来理解 TCE 在生物炭上的吸附机制。在 8-10 小时的平衡时间内,高达 69%的 TCE 从水中被去除。在 700°C 下生产的生物炭比在 300°C 下生产的生物炭更有效。与 P-300 和 S-300 相比,P-700 和 S-700 的摩尔 H/C 和 O/C 较低,导致其具有较高的芳香度和较低的极性,同时具有较高的表面积和较高的吸附能力。准二级和内扩散模型很好地拟合了动力学数据,表明 TCE 吸附到生物炭上的主要机制是化学吸附和孔扩散。

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