State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Dayangfang 8, Beijing 100012, PR China; Department of Chemical Engineering, Tokyo University of Agriculture and Technology, 2-24-16 Naka, Koganei, Tokyo 184-8588, Japan.
State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Dayangfang 8, Beijing 100012, PR China.
Chemosphere. 2018 Aug;204:371-377. doi: 10.1016/j.chemosphere.2018.04.067. Epub 2018 Apr 13.
To examine the Sb(III) retention by three soils with different properties (Ferrosol, Primosol and Isohumosol), kinetic batch experiments were carried out for Sb(III) adsorption-desorption, followed by Sb release using a sequential extraction procedure. In addition, hydroxides, organic matter, and humic substances were selectively removed by washing the soil with oxalate, sodium dithionate-citrate-bicarbonate, HO, and NaOH. The effects of removing these substances on Sb(III) retention were investigated by comparing the Sb distribution coefficients and desorption rates. The results indicated that exogenous Sb(III) was adsorbed onto all three soils rapidly at first and then more slowly. After 168 h of adsorption, most of the adsorbed Sb(III) was irreversibly retained in stable fractions by the Ferrosol. Oxidation reactions negatively affected Sb(III) retention by the Primosol and Isohumosol, and a large proportion of the Sb adsorbed remained mobilizable. The oxalate washing markedly enhanced Sb retention but the sodium dithionate-citrate-bicarbonate washing decreased Sb retention in all three soils. The HO and NaOH washings affected Sb retention by the Ferrosol more than Sb retention by the Primosol and Isohumosol. Changes in the pH and hydroxides caused by the washing strongly affected Sb sorption-desorption. The results improve our understanding of the mobility and bioavailability of exogenous Sb(III) in soils and might benefit future remediation option of Sb-contaminated soils.
为了研究三种具有不同性质的土壤(铁铝土、原始土和均腐殖土)对 Sb(III) 的保留作用,进行了 Sb(III)吸附-解吸的动力学批量实验,随后使用连续提取程序释放 Sb。此外,通过用草酸盐、连二亚硫酸钠-柠檬酸盐-碳酸氢盐、HO 和 NaOH 洗涤土壤,选择性地去除了氢氧化物、有机物和腐殖质。通过比较 Sb 分配系数和解吸率,研究了去除这些物质对 Sb(III)保留的影响。结果表明,外源 Sb(III)最初迅速被三种土壤吸附,然后吸附速度较慢。在吸附 168 h 后,大部分 Sb(III)被铁铝土不可逆地保留在稳定相中。氧化反应对原始土和均腐殖土中 Sb(III)的保留产生负面影响,大部分吸附的 Sb 仍然具有流动性。草酸盐洗涤显著增强了 Sb 的保留,但在三种土壤中,连二亚硫酸钠-柠檬酸盐-碳酸氢盐洗涤降低了 Sb 的保留。HO 和 NaOH 洗涤对铁铝土中 Sb 的保留影响大于原始土和均腐殖土中 Sb 的保留。洗涤引起的 pH 值和氢氧化物的变化强烈影响 Sb 的吸附-解吸。这些结果提高了我们对土壤中外源 Sb(III)的迁移性和生物可利用性的理解,可能有助于未来 Sb 污染土壤的修复选择。