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负载磷的椰子生物炭:一种用于修复镉污染和提高土壤肥力的新策略。

Phosphorus-loaded coconut biochar: A novel strategy for cadmium remediation and soil fertility enhancement.

机构信息

School of Tropical Agriculture and Forestry, Hainan University, Danzhou 571700, China; Key Laboratory of Agro-Forestry Environmental Processes and Ecological Regulation of Hainan Province, School of Environmental Science and Engineering, Hainan University, Haikou 570228, China.

School of Tropical Agriculture and Forestry, Hainan University, Danzhou 571700, China.

出版信息

Ecotoxicol Environ Saf. 2024 Oct 15;285:117074. doi: 10.1016/j.ecoenv.2024.117074. Epub 2024 Sep 28.

Abstract

The management of cadmium (Cd) contamination in soils poses a significant environmental challenge. This study investigates the effectiveness of phosphorus (P)-loaded coconut biochar, synthesized at various pyrolysis temperatures (450°C, 500°C, 550°C, and 600°C), in immobilizing Cd and enhancing P availability in soil environments. The biochar underwent a series of treatments including activation and P enrichment, followed by incubation trials to evaluate its performance in Cd immobilization and P bioavailability enhancement across varying soil concentrations (0.5 %, 1.0 %, and 2.0 %) over time periods of 15, 30, and 45 days. Remediation progress was monitored using phytotoxicity assessments with radish (Raphanus sativus) root length as a bioindicator, supplemented by urease activity analyses. Notably, the activation process increased the P loading capacity of biochar produced at 450°C, 500°C, and 550°C by 54.6 %, 72.4 %, and 51.8 %, respectively, while reducing the P retention capacity of biochar prepared at 600°C by 31.0 %. The biochar activated at 550°C presented the highest efficiency in remediating Cd-contaminated soils. Key findings indicate that the enhanced specific surface area and oxygenated functional group content of the activated biochar facilitated Cd adsorption and P uptake. The P-loaded biochar exhibited a substantial adsorption capacity for Cd, particularly effective at lower concentrations, rendering it highly suitable for soil remediation purposes. Additionally, the study revealed that the application of biochar led to an increase in soil pH, resulting in precipitation of Cd as hydroxide species and formation of insoluble complexes with phosphate ions, thereby reducing its bioavailability. In summary, incorporating P-loaded biochar into soil significantly improved soil quality and enhanced Cd passivation in contaminated soils. The utilization of biochar produced at 550°C, which exhibited optimal performance, suggests a practical and sustainable approach for soil remediation. Future research endeavors should prioritize the refinement of the biochar production process to enhance cost-effectiveness while maintaining high P loading efficiency.

摘要

土壤中镉(Cd)污染的治理是一个重大的环境挑战。本研究探讨了在不同热解温度(450°C、500°C、550°C 和 600°C)下合成的负载磷(P)的椰子生物炭在固定土壤环境中的 Cd 和提高 P 有效性方面的有效性。生物炭经过一系列处理,包括活化和 P 富集,然后进行孵育试验,以评估其在不同土壤浓度(0.5%、1.0%和 2.0%)下固定 Cd 和提高 P 生物有效性的性能,时间跨度为 15、30 和 45 天。通过使用萝卜(Raphanus sativus)根长作为生物指示剂的植物毒性评估和脲酶活性分析来监测修复进展。值得注意的是,活化过程分别将 450°C、500°C 和 550°C 下制备的生物炭的 P 负载能力提高了 54.6%、72.4%和 51.8%,而将 600°C 下制备的生物炭的 P 保留能力降低了 31.0%。在修复 Cd 污染土壤方面,550°C 下活化的生物炭效率最高。主要发现表明,活化生物炭的比表面积和含氧官能团含量增加促进了 Cd 的吸附和 P 的吸收。负载 P 的生物炭对 Cd 具有很强的吸附能力,在较低浓度下尤其有效,非常适合土壤修复目的。此外,该研究表明,生物炭的应用会导致土壤 pH 值升高,从而导致 Cd 以氢氧化物形式沉淀,并与磷酸盐离子形成不溶性络合物,从而降低其生物有效性。总之,将负载 P 的生物炭掺入土壤中可显著改善土壤质量,并增强污染土壤中 Cd 的钝化作用。利用在 550°C 下表现出最佳性能的生物炭为污染土壤的修复提供了一种实用且可持续的方法。未来的研究工作应优先考虑改进生物炭的生产工艺,以提高成本效益,同时保持高的 P 负载效率。

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