Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008, China.
Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008, China; University of Chinese Academy of Sciences, Beijing, 100049, China.
Ecotoxicol Environ Saf. 2020 Oct 1;202:110887. doi: 10.1016/j.ecoenv.2020.110887. Epub 2020 Jun 22.
Chemical immobilization of heavy metals is a simple, low-cost, and environment-friendly technology for remediation of heavy metals contaminated soils. However, changes in environmental conditions, such as water management, acid deposition, temperature fluctuation, etc., might result in release of metal ions from the fixation sites, and the long-term stability of immobilization remediation is unclear. This study attempted to investigate the impact of water management strategies (wetting-drying cycle and dry cycle) on the stability of heavy metal immobilization by one-time application of biochar during 3 consecutive years of rice-wheat crop in Cu/Cd-contaminated soil. The transformation and accumulation of Cd and Cu in soil-crop system and the morphololgy and composition of biochar were analyzed. The results revealed that wetting-drying cycle and drying treatments reduced the contents of available Cd and Cu in soil by 15.9%-17.7% and 23.9%-31.5% and by 19.8%-62.7% and 16.1%-65.0%, as well as increased soil pH by 0.11-0.31 and 0.17-0.56, respectively. In the wetting-drying cycle treatment, biochar was more favorable for decrease in Cd and Cu accumulation in crop, when compared with that in dry treatment; however, the differences were insignificant in the subsequent years. Although the different water management strategies had no obvious effect on the soil total C, physicochemical analysis of the biochar collected after pot experiments indicated that the obvious structural decomposition of biochar in the drying treatment may have resulted in the release of heavy metals immobilized in biochar. These findings help in better understanding of the long-term immobilization mechanism of biochar in soil-plant system.
化学固定化重金属是一种简单、低成本、环保的技术,可用于修复重金属污染土壤。然而,环境条件的变化,如水分管理、酸沉降、温度波动等,可能导致金属离子从固定点释放,固定化修复的长期稳定性尚不清楚。本研究试图探讨一次性施用生物炭对水分管理策略(干湿循环和干循环)对重金属固定化稳定性的影响,在连续 3 年的水稻-小麦作物中,在 Cu/Cd 污染土壤中。分析了土壤-作物系统中 Cd 和 Cu 的转化和积累以及生物炭的形态和组成。结果表明,干湿循环和干燥处理分别降低了土壤中有效态 Cd 和 Cu 的含量 15.9%-17.7%和 23.9%-31.5%,以及 19.8%-62.7%和 16.1%-65.0%,土壤 pH 值分别增加了 0.11-0.31 和 0.17-0.56。在干湿循环处理中,与干燥处理相比,生物炭更有利于降低作物中 Cd 和 Cu 的积累,但在随后的几年中差异不显著。尽管不同的水分管理策略对土壤总 C 没有明显影响,但对盆栽试验后收集的生物炭进行理化分析表明,干燥处理中生物炭的明显结构分解可能导致固定在生物炭中的重金属释放。这些发现有助于更好地理解生物炭在土壤-植物系统中的长期固定化机制。