School of Environment, Nanjing Normal University, Nanjing 210023, China; Department of Chemical Engineering, Tokyo University of Agriculture and Technology, 2-24-16 Naka, Koganei, Tokyo 184-8588, Japan.
DOWA ECO-SYSTEM CO., LTD., Japan.
Sci Total Environ. 2020 Jul 1;724:138203. doi: 10.1016/j.scitotenv.2020.138203. Epub 2020 Mar 24.
Although the deep-layer sedimentary soils excavated from construction sites contain low level of geogenic arsenic (As), remediation is necessary when the As leachability exceeds the environmental standard (10 μg/L) in Japan. In this study, the zero-valent iron (ZVI) amendment followed by dry magnetic separation (ZVI-DMS) was implemented for the treatment of a geogenic As-contaminated alkaline sedimentary soil (pH 8.9; 7.5 mg/kg of total As; 0.33 mg/kg of water-extractable As). This technology involves pH adjustment (adding HSO), ZVI addition, water content reduction (adding water adsorbent CaSO·0.5HO), and dry magnetic separation. The short-term and long-term As leachability before and after treatment was compared using sequential water leaching tests (SWLT). The results illustrated that As could be removed from the bulk soil through the magnetic separation of As-ZVI complexes, although the amount was limited (about 2% of total As). Moreover, immobilization played a dominant role in suppressing As leaching. The HSO addition decreased pH to a circumneutral range and thereby suppress As release. The CaSO·0.5HO addition also contributed to the pH decrease and reduced As leachability. Besides, CaSO·0.5HO-dissolution released Ca that favored As adsorption, and enhanced dissolved organic carbon (DOC) coagulation that decelerated As dissolution. SWLT results indicated that As leachability from remediated soil satisfied the environmental standard (10 μg/L) in both short-term and long-term perspective. However, the secular stability of treated soil deserves more attention due to the easy re-release of As caused by As-bearing framboidal pyrite oxidation. Additionally, during ZVI-DMS process, there is a need to scientifically decide the dosage of ZVI to avoid excessive addition. Our results demonstrated that ZVI-DMS technology could be a promising remediation strategy for geogenic As contaminated sedimentary soils/rocks.
尽管来自建筑工地的深层沉积土壤中含有低水平的原生砷(As),但当日本的 As 浸出率超过环境标准(10μg/L)时,就需要进行修复。在本研究中,采用零价铁(ZVI)改良剂后进行干法磁选(ZVI-DMS)来处理受原生砷污染的碱性沉积土壤(pH 8.9;总 As 含量 7.5mg/kg;可水提取的 As 含量 0.33mg/kg)。该技术涉及 pH 值调整(添加 HSO)、ZVI 添加、含水量降低(添加水吸附剂 CaSO·0.5HO)和干法磁选。通过顺序水浸出试验(SWLT)比较了处理前后短期和长期的 As 浸出率。结果表明,尽管去除量有限(约占总 As 的 2%),但可以通过磁选将 As-ZVI 复合物从土壤本体中去除。此外,固定化在抑制 As 浸出方面起主导作用。添加 HSO 将 pH 值降低至近中性范围,从而抑制 As 的释放。添加 CaSO·0.5HO 也有助于降低 pH 值并减少 As 的浸出率。此外,CaSO·0.5HO 的溶解会释放出有利于 As 吸附的 Ca,并促进溶解有机碳(DOC)的凝结,从而减缓 As 的溶解。SWLT 结果表明,从修复土壤中浸出的 As 在短期和长期内均满足环境标准(10μg/L)。然而,由于含 As 的莓状黄铁矿氧化导致 As 易重新释放,处理土壤的长期稳定性值得进一步关注。此外,在 ZVI-DMS 过程中,需要科学决定 ZVI 的用量,以避免过度添加。研究结果表明,ZVI-DMS 技术可能是一种有前途的修复受原生砷污染的沉积土壤/岩石的策略。