Sun Lina, Chen Su, Chao Lei, Sun Tieheng
Key Laboratory of Environment Engineering of Shenyang University, Shenyang 110044, China.
Bull Environ Contam Toxicol. 2007 Nov;79(5):514-8. doi: 10.1007/s00128-007-9274-8. Epub 2007 Oct 9.
Artificially contaminated soils (A, B) and naturally contaminated soil (S2) in China were used as the tested soils, and the effect of continuous flooding on the changes of Eh, pH and the speciation of cadmium, lead in contaminated soils was studied in the paper. The results indicated that soil Eh decreased with flooding time, and that soil pH increased with flooding time. The changes of soil pH ceased after 60 days of submergence. The exchangeable Cd and Pb decreased obviously during the flooding process from the results of five-step sequential extraction. The calculations of mobility factor (MF) showed that Cd mobility significantly decreased in artificially contaminated soils (A, B) after the flood. But the change of Pb mobility was not significant after the flood, although a decrease of Pb concentration in the exchangeable fraction (SE) was observed.
采用中国的人工污染土壤(A、B)和天然污染土壤(S2)作为受试土壤,研究了持续淹水对污染土壤中氧化还原电位(Eh)、pH值以及镉、铅形态变化的影响。结果表明,土壤Eh随淹水时间的延长而降低,土壤pH值随淹水时间的延长而升高。淹水60天后土壤pH值变化停止。五步连续提取结果表明,淹水过程中可交换态镉和铅明显减少。迁移率因子(MF)计算结果表明,淹水后人工污染土壤(A、B)中镉的迁移率显著降低。虽然观察到可交换态铅(SE)中铅浓度有所下降,但淹水后铅迁移率的变化并不显著。