Can the aging process necessarily weaken the effect of biochar on cadmium-contaminated soil remediation: considering biochar at different pyrolysis temperatures and aging treatment.

IF 3.2 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL
Jianxin Fan, Ting Duan, Xingyu Wu, Maoyu Liao, Jiaoxia Sun
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Abstract

Biochar has widely used to immobilize soil heavy metals in recent years, while the properties of biochar varied with environmental conditions. The influence of biochar aging on fixation and speciation transformation of Cd in soil remains unclear. This study explores how biochar aging affects the fixation and speciation transformation of Cd in soil. Rice straw biochar (RBC) prepared at different pyrolysis temperatures (300 °C, 500 °C, and 700 °C) was aged under three treatments (drying and watering cycle (DW), H2O2 oxidation (HO), and citric acid acidification (CA)) to investigate the effects of the aging process on the adsorption and passivation capacity for Cd. Results showed that the aging treatment increased Cd adsorption on RBC300 by 73.69% to 216.15%, while adsorption on RBC500 and RBC700 decreased by 11.52% to 74.56% and 7.40% to 75.89%, respectively. The addition of both fresh and aged RBC raised pH, DOC, and TOC in Cd-contaminated soil, aiding in Cd fixation. Either fresh or aged RBC addition enhance the stability of Cd in soil. Compared to CK treatment, residual Cd content rose by 28.63% to 43.71%, while both acid-extractable and reducible Cd contents decreased by 9.144% to 10.95%. Furthermore, the available Cd content in the soil saw a reduction of 10.45% to 30.77%, and high-temperature pyrolytic RBC exhibited a stronger capacity for Cd passivation in the soil. Both fresh and aged RBC indirectly reduced Cd bioavailability by affecting soil pH, DOC, and TOC, and the nature aging process (DW) did not weaken the effect of biochar on Cd-contaminated soil remediation. Thus, biochar has a long-term potential for mitigating Cd pollution in farmland.

老化过程是否一定会削弱生物炭对镉污染土壤的修复效果:考虑不同热解温度和老化处理的生物炭。
近年来,生物炭被广泛用于固定土壤中的重金属,而生物炭的性质随环境条件的变化而变化。生物炭老化对土壤中镉的固定和种类转化的影响仍不清楚。本研究探讨了生物炭的老化如何影响土壤中镉的固定和种类转化。在不同的热解温度(300 °C、500 °C、700 °C)下制备的稻草生物炭(RBC)在三种处理(干燥和浇水循环(DW)、H2O2 氧化(HO)、柠檬酸酸化(CA))下进行老化,以研究老化过程对镉的吸附和钝化能力的影响。结果表明,老化处理使 RBC300 对镉的吸附量增加了 73.69% 至 216.15%,而 RBC500 和 RBC700 对镉的吸附量则分别减少了 11.52% 至 74.56% 和 7.40% 至 75.89%。添加新鲜和陈化的 RBC 都能提高镉污染土壤的 pH 值、DOC 和 TOC,有助于镉的固定。无论是添加新鲜还是陈化的 RBC,都能提高镉在土壤中的稳定性。与 CK 处理相比,残余镉含量上升了 28.63% 至 43.71%,而酸萃取镉和还原镉含量则下降了 9.144% 至 10.95%。此外,土壤中的可利用镉含量降低了 10.45% 至 30.77%,高温热解 RBC 对土壤中镉的钝化能力更强。新鲜和老化的 RBC 都通过影响土壤 pH 值、DOC 和 TOC 间接降低了镉的生物利用率,而自然老化过程(DW)并没有削弱生物炭对镉污染土壤的修复效果。因此,生物炭具有减轻农田镉污染的长期潜力。
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来源期刊
Environmental Geochemistry and Health
Environmental Geochemistry and Health 环境科学-工程:环境
CiteScore
8.00
自引率
4.80%
发文量
279
审稿时长
4.2 months
期刊介绍: Environmental Geochemistry and Health publishes original research papers and review papers across the broad field of environmental geochemistry. Environmental geochemistry and health establishes and explains links between the natural or disturbed chemical composition of the earth’s surface and the health of plants, animals and people. Beneficial elements regulate or promote enzymatic and hormonal activity whereas other elements may be toxic. Bedrock geochemistry controls the composition of soil and hence that of water and vegetation. Environmental issues, such as pollution, arising from the extraction and use of mineral resources, are discussed. The effects of contaminants introduced into the earth’s geochemical systems are examined. Geochemical surveys of soil, water and plants show how major and trace elements are distributed geographically. Associated epidemiological studies reveal the possibility of causal links between the natural or disturbed geochemical environment and disease. Experimental research illuminates the nature or consequences of natural or disturbed geochemical processes. The journal particularly welcomes novel research linking environmental geochemistry and health issues on such topics as: heavy metals (including mercury), persistent organic pollutants (POPs), and mixed chemicals emitted through human activities, such as uncontrolled recycling of electronic-waste; waste recycling; surface-atmospheric interaction processes (natural and anthropogenic emissions, vertical transport, deposition, and physical-chemical interaction) of gases and aerosols; phytoremediation/restoration of contaminated sites; food contamination and safety; environmental effects of medicines; effects and toxicity of mixed pollutants; speciation of heavy metals/metalloids; effects of mining; disturbed geochemistry from human behavior, natural or man-made hazards; particle and nanoparticle toxicology; risk and the vulnerability of populations, etc.
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