Institute of Organic Contaminant Control and Soil Remediation, College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing 210095, China.
Int J Environ Res Public Health. 2018 Aug 13;15(8):1731. doi: 10.3390/ijerph15081731.
Co-contaminated soils containing heavy metals and polycyclic aromatic hydrocarbons (PAHs) are an environmental and human health risk. Research into the remediation of these soils is imperative. In this paper, a novel investigation utilizing calcination technique to stabilize heavy metals and simultaneously remove PAHs in soil was conducted. Calcination temperature (300⁻700 °C) was observed to play a dominant role in heavy metal stabilization and PAH removal in soils. However, calcination time (0.5⁻8 h) had no significant effect on these contaminants during calcination at different temperatures. Considering the remediation cycle requirements and economic costs of engineering, we suggested that the optimal calcination condition for Zn, Cu, naphthalene, and fluoranthene was at 700 °C for 0.5 h, and the corresponding stabilization or removal efficiency values were 96.95%, 98.41%, 98.49%, and 98.04%, respectively. Results indicate that calcination as a remedial strategy exhibits a bright future for practical applications in the simultaneous stabilization of heavy metals and PAH removal from co-contaminated sites.
同时含有重金属和多环芳烃(PAHs)的污染土壤对环境和人体健康存在风险。因此,对这些土壤的修复研究势在必行。本文采用煅烧技术对重金属进行稳定化处理,同时去除土壤中的多环芳烃,这是一种新颖的研究。煅烧温度(300-700℃)在重金属稳定化和土壤中多环芳烃去除方面起着重要作用。然而,在不同温度下煅烧时,煅烧时间(0.5-8 小时)对这些污染物没有显著影响。考虑到修复周期要求和工程经济成本,我们建议 Zn、Cu、萘和荧蒽的最佳煅烧条件为 700℃,煅烧 0.5 小时,相应的稳定化或去除效率值分别为 96.95%、98.41%、98.49%和 98.04%。结果表明,煅烧作为一种修复策略,在同时稳定重金属和去除多环芳烃方面具有广阔的应用前景。