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废水热解水凝胶吸附剂用于镉分离和生物炭再生。

Pyrolysis of exhausted hydrochar sorbent for cadmium separation and biochar regeneration.

机构信息

School of Environmental Science and Engineering/ Tianjin Key Lab of Biomass Waste Utilization, Tianjin University, Tianjin, 300072, China.

Key Laboratory of Advanced Process Control for Light Industry, Ministry of Education, Jiangnan University, Wuxi, 214122, China.

出版信息

Chemosphere. 2022 Nov;306:135546. doi: 10.1016/j.chemosphere.2022.135546. Epub 2022 Jun 28.

Abstract

Sorption is considered a cost-effective technique for cadmium (Cd) removal from water, while the exhausted Cd-enriched sorbent should be properly disposed of. In this study, pyrolysis of exhausted hydrochar sorbent was conducted at 300-900 °C, and the behavior of Cd and the physicochemical properties and environmental applications of the regenerated biochar were investigated. The vaporization of adsorbed Cd in hydrochar was greatly enhanced by elevating pyrolysis temperature, and almost no Cd was observed in the regenerated biochars obtained at 700-900 °C. In comparison with the raw hydrochar, the regenerated biochars showed higher pH, ash content, and carbon content, while the contents of hydrogen and oxygen decreased. According to the toxicity characteristic leaching procedure result, the toxicity and mobility of Cd in hydrochar were greatly reduced after pyrolysis. Notably, the regenerated biochar showed much higher Cd sorption capacity (26.05-30.24 mg/g) than the raw hydrochar (6.70 mg/g). Surface complexation with oxygen-containing functional groups was the dominant Cd sorption mechanism for hydrochar, and precipitation between Cd and carbonates dominated the Cd removal by the regenerated biochars. These results illuminated that pyrolysis can be an effective technique for the harmless disposal of exhausted hydrochar sorbent and the regeneration of valuable biochar.

摘要

吸附被认为是一种从水中去除镉 (Cd) 的经济有效的技术,而富含 Cd 的废弃吸附剂则应妥善处理。在这项研究中,在 300-900°C 下对废弃水凝胶吸附剂进行热解,并研究了 Cd 的行为以及再生生物炭的物理化学性质和环境应用。升高热解温度大大增强了水凝胶中吸附 Cd 的挥发,在 700-900°C 下获得的再生生物炭中几乎没有观察到 Cd。与原始水凝胶相比,再生生物炭表现出更高的 pH 值、灰分含量和碳含量,而氢和氧的含量则降低。根据毒性特征浸出程序的结果,热解大大降低了水凝胶中 Cd 的毒性和迁移性。值得注意的是,再生生物炭的 Cd 吸附容量(26.05-30.24mg/g)明显高于原始水凝胶(6.70mg/g)。含氧官能团的表面络合是水凝胶中 Cd 吸附的主要机制,而 Cd 与碳酸盐之间的沉淀则主导了再生生物炭对 Cd 的去除。这些结果表明,热解可以有效地处理废弃水凝胶吸附剂并再生有价值的生物炭。

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