Beiyuan Jingzi, Tsang Daniel C W, Ok Yong Sik, Zhang Weihua, Yang Xin, Baek Kitae, Li Xiang-Dong
Department of Civil and Environmental Engineering, The Hong Kong Polytechnic University, Hung Hom, Kowloon, Hong Kong, China.
Department of Civil and Environmental Engineering, The Hong Kong Polytechnic University, Hung Hom, Kowloon, Hong Kong, China.
Chemosphere. 2016 Sep;159:426-432. doi: 10.1016/j.chemosphere.2016.06.030. Epub 2016 Jun 20.
While chelant-enhanced soil washing has been widely studied for metal extraction from contaminated soils, there are concerns about destabilization and leaching of residual metals after remediation. This study integrated 2-h soil washing enhanced by biodegradable ethylenediaminedisuccinic acid (EDDS) and 2-month stabilization using agricultural waste product (soybean stover biochar pyrolyzed at 300 and 700 °C), industrial by-product (coal fly ash (CFA)), and their mixture. After integration with 2-month stabilization, the leachability and mobility of residual metals (Cu, Zn, and Pb) in the field-contaminated soil were significantly reduced, especially for Cu, in comparison with 2-h EDDS washing alone. This suggested that the metals destabilized by EDDS-washing could be immobilized by subsequent stabilization with biochar and CFA. Moreover, when the remediation performance was evaluated for phytoavailability and bioaccessibility, prior EDDS washing helped to achieve a greater reduction in the bioavailable fraction of metals than sole stabilization treatment. This was probably because the weakly-bound metals were first removed by EDDS washing before stabilization. Both individual and combined applications of biochar and CFA showed comparable effectiveness regardless of the difference in material properties, possibly due to the high level of amendments (150 ton ha(-1)). Based on the mobility and bioaccessibility results, the estimated human health risk (primarily resulting from Pb) could be mitigated to an acceptable level in water consumption pathway or reduced by half in soil ingestion pathway. These results suggest that an integration of EDDS washing with soil stabilization can alleviate post-remediation impacts of residual metals in the treated soil.
虽然螯合剂强化土壤淋洗技术已被广泛研究用于从污染土壤中提取金属,但人们担心修复后残留金属的稳定性和淋溶问题。本研究结合了可生物降解的乙二胺二琥珀酸(EDDS)强化2小时的土壤淋洗以及使用农业废弃物(300℃和700℃热解的大豆秸秆生物炭)、工业副产品(粉煤灰(CFA))及其混合物进行2个月的稳定化处理。与仅进行2小时的EDDS淋洗相比,经过2个月的稳定化处理后,现场污染土壤中残留金属(铜、锌和铅)的淋溶性和迁移性显著降低,尤其是铜。这表明,经EDDS淋洗而不稳定的金属可通过随后用生物炭和CFA进行稳定化处理而被固定。此外,在评估植物有效性和生物可及性的修复性能时,预先进行EDDS淋洗比单独的稳定化处理能使金属的生物可利用部分有更大程度的减少。这可能是因为在稳定化处理之前,弱结合态金属首先被EDDS淋洗去除。无论材料性质有何差异,生物炭和CFA单独及联合应用均显示出相当的效果,这可能是由于改良剂用量较高(150吨公顷-1)。根据迁移性和生物可及性结果,在饮水途径中,估计的人类健康风险(主要由铅引起)可降低到可接受水平,或在土壤摄入途径中降低一半。这些结果表明,将EDDS淋洗与土壤稳定化相结合可以减轻处理后土壤中残留金属的修复后影响。