College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing, 210095, China.
College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing, 210095, China.
Environ Pollut. 2019 Aug;251:952-960. doi: 10.1016/j.envpol.2019.05.086. Epub 2019 May 17.
Arsenic (As) tends to mobilize in flooded paddy soil due to the reductive dissolution of the iron (oxyhydr)oxides to which As sorbs, resulting in elevated As accumulation in rice that poses a potential risk to the food safety and human health. Microbial sulfate reduction is an important biogeochemical process in paddy soils, but its impact on As mobilization remains poorly understood. In this study, we incubated eight As-contaminated paddy soils under flooded conditions to investigate the effect of sulfate addition on As mobility. Porewater Fe and As concentrations and As species were determined. Among the eight soils, an addition of 50 mg S kg as sodium sulfate decreased porewater arsenite only in two soils, which also showed a high mobilization of Fe. Further experiments showed that the addition of sulfate to these two soils stimulated microbial sulfate reduction but decreased porewater concentrations of both arsenite and Fe. Additionally, the supply of sulfate increased the fractions of As associated with acid volatile sulfides in the solid phase and decreased As uptake by rice in pot experiments under similar conditions. The effect of sulfate addition on porewater As was diminished by the addition of molybdate, an inhibitor of sulfate reducing bacteria. These results suggest the formation of secondary FeS minerals which co-precipitate or sorb arsenite as a likely mechanism of As immobilization, which was also supported by thermodynamic modeling of the pore water. Thus, sulfate additions can immobilize As and reduce its availability to rice plants in paddy soils containing a high potential for microbial Fe reduction, providing an efficient way to mitigate the As transfer to the food chain.
砷(As)由于吸附在铁(氧)氢氧化物上的铁的还原溶解而在淹水稻田中移动,导致水稻中砷的积累增加,对食品安全和人类健康构成潜在风险。微生物硫酸盐还原是稻田中一种重要的生物地球化学过程,但它对砷迁移的影响仍知之甚少。在这项研究中,我们在淹水条件下培养了 8 种砷污染的稻田土壤,以研究硫酸盐添加对砷迁移性的影响。测定了孔隙水铁和砷浓度和砷形态。在这 8 种土壤中,添加 50mgSkg-1 的硫酸钠仅降低了两种土壤的孔隙水中亚砷酸盐,这两种土壤的铁也表现出高迁移性。进一步的实验表明,硫酸盐的添加刺激了这两种土壤中的微生物硫酸盐还原,但降低了孔隙水中亚砷酸盐和铁的浓度。此外,在类似条件下的盆栽实验中,硫酸盐的供应增加了固相中与酸可挥发硫化物结合的砷分数,并降低了砷在水稻中的吸收。钼酸盐(硫酸盐还原细菌的抑制剂)的添加减少了硫酸盐添加对孔隙水中 As 的影响。这些结果表明,形成次生 FeS 矿物可能是 As 固定的一种机制,这些矿物共同沉淀或吸附亚砷酸盐,这也得到了孔隙水热力学模型的支持。因此,硫酸盐的添加可以固定砷,降低其在含有高微生物铁还原潜力的稻田土壤中对水稻植物的有效性,为减轻砷向食物链的转移提供了一种有效途径。