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原位固化/稳定化与化学氧化联合修复土壤中潜在有毒金属和有机复合污染:效果、机制与评价。

Remediating Potentially Toxic Metal and Organic Co-Contamination of Soil by Combining In Situ Solidification/Stabilization and Chemical Oxidation: Efficacy, Mechanism, and Evaluation.

机构信息

School of Chemical and Environmental Engineering, China University of Mining and Technology (Beijing), Beijing 100083, China.

State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Science, Beijing 100012, China.

出版信息

Int J Environ Res Public Health. 2018 Nov 20;15(11):2595. doi: 10.3390/ijerph15112595.

DOI:10.3390/ijerph15112595
PMID:30463391
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC6266821/
Abstract

Most soil remediation studies investigated single contaminants or multiple contaminants of the same type. However, in field conditions, soils are often contaminated with potentially both toxic metals and organic pollutants, posing a serious technical challenge. Here, batch experiments were conducted to evaluate the performance of combining in situ solidification/stabilization (ISS) and in situ chemical oxidation (ISCO) for the simultaneous removal of aniline (1000 mg/kg) and Cd (10 mg/kg). All four tested ISS amendments, especially quick lime and Portland cement, promoted in situ chemical oxidation with activated persulfate in contaminated soil. Combined ISS/ISCO remediation effectively removed aniline and reduced the bioavailable Cd content at optimal initial persulfate and ISS amendment concentrations of 1.08 mol/kg and 30 wt% with a seven-day curing time, and significantly reduced leaching. Persulfate inhibited the reduction of the bioavailable Cd content, and ISS amendment with persulfate did not synergistically remediate Cd in co-contaminated soil. Strong alkalinity and high temperature were the main mechanisms driving rapid pollutant removal and immobilization. The reaction of CaO with water released heat, and Ca(OH)₂ formation increased the pH. The relative contributions of heat vs. alkaline activation, as well as the contaminant removal efficiency, increased with ISS amendment CaO content. Combined treatment altered the soil physicochemical properties, and significantly increased Ca and S contents. Activated persulfate-related reactions did not negatively impact unconfined compressive strength and hydraulic conductivity. This work improves the selection of persulfate activation methods for the treatment of soils co-contaminated with both potentially toxic metals and organic pollutants.

摘要

大多数土壤修复研究都调查了单一污染物或同一类型的多种污染物。然而,在野外条件下,土壤通常同时受到有毒金属和有机污染物的污染,这是一个严重的技术挑战。在这里,进行了批量实验,以评估原位固化/稳定化(ISS)和原位化学氧化(ISCO)相结合同时去除苯胺(1000mg/kg)和 Cd(10mg/kg)的性能。所有四种测试的 ISS 改良剂,特别是生石灰和波特兰水泥,都促进了受污染土壤中活性过硫酸盐的原位化学氧化。在最优的初始过硫酸盐和 ISS 改良剂浓度(1.08mol/kg 和 30wt%)下,结合 ISS/ISCO 修复可有效去除苯胺,并降低生物可利用 Cd 的含量,养护期为 7 天,显著降低浸出。过硫酸盐抑制了生物可利用 Cd 含量的降低,而过硫酸盐和 ISS 改良剂并没有协同修复共存污染土壤中的 Cd。强碱性和高温是驱动快速污染物去除和固定的主要机制。CaO 与水的反应释放热量,而 Ca(OH)₂的形成增加了 pH 值。热与碱性激活的相对贡献以及污染物去除效率随着 ISS 改良剂 CaO 含量的增加而增加。联合处理改变了土壤的物理化学性质,并显著增加了 Ca 和 S 的含量。过硫酸盐相关的反应并没有对无侧限抗压强度和水力传导率产生负面影响。这项工作提高了对同时受到有毒金属和有机污染物污染的土壤进行过硫酸盐处理方法的选择。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/0b2be53a2202/ijerph-15-02595-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/9af7ec335b63/ijerph-15-02595-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/dd7866f8335c/ijerph-15-02595-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/f0b7f4fd456d/ijerph-15-02595-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/fad8fb7519d2/ijerph-15-02595-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/7a60371ebb0e/ijerph-15-02595-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/5ebe2f2ceb7b/ijerph-15-02595-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/78f126d01a50/ijerph-15-02595-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/0b2be53a2202/ijerph-15-02595-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/9af7ec335b63/ijerph-15-02595-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/dd7866f8335c/ijerph-15-02595-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/f0b7f4fd456d/ijerph-15-02595-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/fad8fb7519d2/ijerph-15-02595-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/7a60371ebb0e/ijerph-15-02595-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/5ebe2f2ceb7b/ijerph-15-02595-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/78f126d01a50/ijerph-15-02595-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1550/6266821/0b2be53a2202/ijerph-15-02595-g008.jpg

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