Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Ministry of Education, College of Environment, Hohai University, Nanjing 210098, PR China.
Nanjing Institute of Environmental Science, Ministry of Environmental Protection of China, Nanjing 210042, PR China.
Ecotoxicol Environ Saf. 2021 Jan 15;208:111675. doi: 10.1016/j.ecoenv.2020.111675. Epub 2020 Dec 7.
Metal bioavailability controls its behaviors in soil-plant system, especially involved in biochar amendment. This study compared a rhizospheric pore-water extraction against a BCR sequential extraction method to understand cadmium (Cd) bioavailability in two typical Chinese soils. Soils were spiked with five levels of Cd (CdCl) and remediated with 3% corn-straw derived biochar. After 60 days of lettuce growth, Cd accumulation and enzyme activities in tissues were analyzed. Results showed that biochar increased soil properties (pH, CEC and SOM) compared to un-amended soils, but decreased contents of bioavailable Cd in soil pore-water (Cd) and BCR extracted Cd (Cd). Contents of Cd were lower in yellow-brown soils than that in red soils. Pearson analysis showed that bioavailable Cd is negatively correlated with soil pH and CEC (p < 0.05). Cd accumulation in lettuce roots and leaves both were decreased by biochar addition, and the established linear equations proved that soil Cd is the best predictor for Cd accumulation in lettuce roots (r = 0.964) and in leaves (r = 0.953), followed by Cd. Transfer factor (TF) values of Cd from roots to leaves were lower than 1, and slightly better correlated with soil Cd (r = -0.674, p < 0.01) than Cd (r = -0.615, p < 0.01). Aggregated boosted tree (ABT) analyses indicated that soil properties together with Cd contribute more than 50% to root enzyme activities. Collectively, soil Cd is a promising predictor of Cd bioavailability, accumulation and toxicity in soil-plant system with biochar addition.
金属生物可利用性控制其在土壤-植物系统中的行为,特别是在生物炭改良中。本研究比较了根际孔隙水提取和 BCR 连续提取方法,以了解两种典型中国土壤中镉(Cd)的生物可利用性。土壤中添加了五个镉水平(CdCl)并用 3%玉米秸秆衍生生物炭进行修复。在生菜生长 60 天后,分析了组织中 Cd 的积累和酶活性。结果表明,与未添加生物炭的土壤相比,生物炭增加了土壤性质(pH、CEC 和 SOM),但降低了土壤孔隙水中的有效 Cd(Cd)和 BCR 提取的 Cd(Cd)含量。黄棕壤中 Cd 的含量低于红壤。Pearson 分析表明,有效 Cd 与土壤 pH 和 CEC 呈负相关(p < 0.05)。生物炭的添加降低了生菜根和叶中 Cd 的积累,建立的线性方程证明土壤 Cd 是生菜根(r = 0.964)和叶(r = 0.953)中 Cd 积累的最佳预测因子,其次是 Cd。Cd 从根到叶的转移系数(TF)值均小于 1,与土壤 Cd (r = -0.674,p < 0.01)的相关性略好于 Cd (r = -0.615,p < 0.01)。聚合提升树(ABT)分析表明,土壤性质与 Cd 共同对根酶活性的贡献超过 50%。总之,土壤 Cd 是生物炭添加后土壤-植物系统中 Cd 生物可利用性、积累和毒性的有前途的预测因子。