Department of Civil and Environmental Engineering, The Hong Kong Polytechnic University, Hung Hom, Kowloon, Hong Kong.
National Synchrotron Radiation Research Center, 101 Hsin-Ann Road, Hsinchu Science Park, Hsinchu 30076, Taiwan.
Environ Pollut. 2018 Jan;232:375-384. doi: 10.1016/j.envpol.2017.09.040. Epub 2017 Sep 28.
The behaviour of arsenic (As) from geogenic soil exposed to aerobic conditions is critical to predict the impact of As on the environment, which processes remain unresolved. The current study examined the depth profile of As in geologically derived subsoil cores from Hong Kong and investigated the mobilization, plant availability, and bioaccessibility of As in As-contaminated soil at different depths (0-45.8 m). Results indicated significant heterogeneity, with high levels of As in three layers of soil reaching up to 505 mg/kg at a depth of 5 m, 404 mg/kg at a depth of 15 m, and 1510 mg/kg at a depth of 27-32 m. Arsenic in porewater samples was <11.5 μg/L in the study site. X-ray absorption spectroscopy (XAS) indicated that main As species in soil was arsenate (As(V)), as adsorbed fraction to Fe oxides (41-69% on goethite and 0-8% on ferrihydrite) or the mineral form scorodite (30-57%). Sequential extraction procedure demonstrated that 0.5 ± 0.4% of As was exchangeable. Aerobic incubation experiments exhibited that a very small amount (0.14-0.48 mg/kg) of As was desorbed from the soil because of the stable As(V) complex structure on abundant Fe oxides (mainly goethite), where indigenous microbes partly (59 ± 18%) contributed to the release of As comparing with the sterilized control. Furthermore, no As toxicity in the soil was observed with the growth of ryegrass. The bioaccessibility of As was <27% in the surface soil using simplified bioaccessibility extraction test. Our systematic evaluation indicated that As in the geogenic soil profile from Hong Kong is relatively stable exposing to aerobic environment. Nevertheless, children and workers should avoid incidental contact with excavated soil, because high concentration of As was present in the digestive solution (<0.1-268 μg/L).
在有氧条件下,源自地质土壤的砷(As)的行为对预测砷对环境的影响至关重要,但这些过程仍未得到解决。本研究检查了来自香港地质衍生亚土层岩芯中砷的深度分布,并研究了不同深度(0-45.8 m)受污染土壤中砷的迁移、植物可利用性和生物可及性。结果表明存在显著的异质性,在 5 米深处的三层土壤中砷含量高达 505 mg/kg,在 15 米深处达到 404 mg/kg,在 27-32 米深处达到 1510 mg/kg。研究地点的水样中砷的浓度<11.5 μg/L。X 射线吸收光谱(XAS)表明,土壤中的主要砷物种为砷酸盐(As(V)),以吸附在铁氧化物上的形式存在(针铁矿上为 41-69%,水铁矿上为 0-8%)或矿物形式的砷铁矿(30-57%)。连续提取程序表明,0.5±0.4%的砷为可交换态。有氧培养实验表明,由于丰富的铁氧化物(主要是针铁矿)上稳定的 As(V)络合结构,只有极少量(0.14-0.48 mg/kg)的砷从土壤中解吸出来,与灭菌对照相比,土著微生物部分(59±18%)促进了砷的释放。此外,在黑麦草生长的情况下,土壤中没有观察到砷的毒性。使用简化的生物可及性提取试验,表层土壤中砷的生物可及性<27%。我们的系统评估表明,香港地质土壤剖面中的砷在有氧环境下相对稳定。然而,儿童和工人应避免意外接触挖掘出的土壤,因为砷在消化液中的浓度较高(<0.1-268μg/L)。