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利用磷酸改性生物炭降低土壤中钒的浸出潜力和生物可利用性。

Utilization of phosphoric acid-modified biochar to reduce vanadium leaching potential and bioavailability in soil.

机构信息

State Key Laboratory of Geohazard Prevention and Geoenvironment Proctection, Chengdu University of Technology, Chengdu 610059, Sichuan, China; College of Ecology and Environment, Chengdu University of Technology, Chengdu, Sichuan 610059, China.

College of Ecology and Environment, Chengdu University of Technology, Chengdu, Sichuan 610059, China.

出版信息

Environ Pollut. 2024 Mar 1;344:123360. doi: 10.1016/j.envpol.2024.123360. Epub 2024 Jan 15.

Abstract

Remediating vanadium (V) polluted soil has garnered widespread attention over the past decade. Yet, few research projects have investigated the stabilization of soil V using modified biochar, so the effects and interacting mechanisms between soil properties and modified biochar for V immobilization and stabilization remain unclear. Hence, this gap is addressed by determining the leaching behavior and mechanisms of soil V on different dosages of phosphoric acid (HPO) impregnated biochar (MLBC, 0.5%-4%). The applicability and durability in soil V immobilization was investigated under acid precipitation. The MLBC effect on V bioavailability and mobility was assessed first by CaCl, Toxicity Characteristic Leaching Procedure (TCLP) and Synthetic Precipitation Leaching Procedure (SPLP) extractions in different periods. The V concentrations significantly reduced in CaCl, TCLP, and SPLP extract with MLBC at each dosage (30 d), while slight to significant increase in SPLP and TCLP extract V was recorded in a long-term incubation (90 d). Column leaching test further demonstrated the high durability of 4% MLBC in V stabilization under continuous acid exposure. Compared to the control (no-biochar), the accumulated V content in the leaching solution significantly decreased in MLBC-amended soil. Acid soluble fraction of V showed significant negative correlation with both soil organic matter (SOM) and available P, which was positively correlated with pH, suggested that pH, available P and SOM were key factors affecting the bioavailability of V in soil. Moreover, combining with the characterization results of MLBC and amended soil, the results revealed that HPO modified biochar played a vital role on V immobilization and soil improvement by forming electrostatic adsorption, ion exchange, redox reaction or complexation with the increase of functional groups. These revealed an efficient and steady development of soil quality and treatment for soil V contamination, under MLBC operation to soil polluted with exogenous V.

摘要

在过去的十年中,修复钒(V)污染土壤引起了广泛关注。然而,很少有研究项目调查使用改性生物炭稳定土壤 V,因此土壤性质与改性生物炭之间相互作用机制以及对 V 固定和稳定的影响仍不清楚。因此,通过确定不同剂量磷酸(HPO)浸渍生物炭(MLBC,0.5%-4%)对土壤 V 的浸出行为和机制来解决这一差距。在酸雨下研究了 MLBC 在土壤 V 固定中的适用性和耐久性。首先通过 CaCl 2 、毒性特征浸出程序(TCLP)和合成沉淀浸出程序(SPLP)在不同时期提取来评估 MLBC 对 V 生物有效性和迁移性的影响。在每个剂量(30d)下,MLBC 可显著降低 CaCl 2 、TCLP 和 SPLP 提取物中的 V 浓度,而在长期孵育(90d)中,SPLP 和 TCLP 提取物中的 V 浓度则略有增加。柱浸出试验进一步证明了在连续酸暴露下,4%MLBC 对 V 稳定的高耐久性。与对照(无生物炭)相比,在 MLBC 改性土壤中,浸出溶液中的 V 积累量显著减少。V 的酸可溶分数与土壤有机质(SOM)和有效 P 呈显著负相关,与 pH 呈正相关,表明 pH、有效 P 和 SOM 是影响土壤中 V 生物有效性的关键因素。此外,结合 MLBC 和改性土壤的表征结果,结果表明 HPO 改性生物炭通过形成静电吸附、离子交换、氧化还原反应或与功能基团的络合作用,对 V 固定和土壤改良起着重要作用。这些揭示了在 MLBC 作用下,受外源 V 污染的土壤的土壤质量和处理具有高效稳定的发展。

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