Key Laboratory of Materials Physics, Centre for Environmental and Energy Nanomaterials, Anhui Key Laboratory of Nanomaterials and Nanotechnology, Institute of Solid State Physics, Chinese Academy of Sciences, Hefei 230031, China; Institute of Soil and Fertilizer, Anhui Academy of Agricultural Sciences, Hefei 230031, China.
Key Laboratory of Materials Physics, Centre for Environmental and Energy Nanomaterials, Anhui Key Laboratory of Nanomaterials and Nanotechnology, Institute of Solid State Physics, Chinese Academy of Sciences, Hefei 230031, China.
J Hazard Mater. 2016 Mar 5;304:40-8. doi: 10.1016/j.jhazmat.2015.10.048. Epub 2015 Oct 27.
Long-term effect of biochar on PTEs (potential toxic elements) immobilization depends upon biochar own property and its aging process in soil. To understand the role of biachar type on PTEs stabilization, two types of biochar, corn-straw-derived biochar (CB) and hardwood-derived biochar (HB), were compared for their efficacy in achieving a stable decrease in the bio-availability of Cd and Cu in soils. The 3-year pot-culture experiment showed that HB reduced the concentration of CaCl2-extractable Cd and Cu by 57.9 and 63.8% in soil, and Cd and Cu uptake by 63.6 and 56.3% in rice tissue respectively, in the first year, whereas these values increased in the next two years. On the other hand, CB decreased these values steadily year by year. At the end of the 3 years, CB at 5% level had lowered the levels of CaCl2-extractable Cd and Cu by 53.6 and 66.8%, respectively. These variations between CB and HB were due to the differences in the way the two types of biochar age in the soil. The aging process was simulated in the laboratory, and the XPS results showed that the oxidization of the biochars introduced more oxygen-containing groups (especially carboxyl) on the surface of CB than HB, leading to a correspondingly greater number of oxygenated binding sites for Cd and Cu in the case of CB. The content of lignin was the major factor resulting in the variation of oxidation degree in two biochars. These results suggest that it is important to select the right kind of biochar to stably decrease the bio-availability of potential toxic elements (Cd and Cu) in contaminated soils.
生物炭对 PTEs(潜在有毒元素)固定的长期影响取决于生物炭自身的性质及其在土壤中的老化过程。为了了解生物炭类型对 PTEs 稳定性的作用,比较了两种生物炭,即玉米秸秆衍生生物炭(CB)和硬木衍生生物炭(HB),以评估它们在降低土壤中 Cd 和 Cu 生物有效性方面的效果。为期 3 年的盆栽培养实验表明,HB 在第一年将土壤中可提取的 CaCl2-Cd 和 Cu 的浓度降低了 57.9%和 63.8%,同时将水稻组织中 Cd 和 Cu 的吸收量降低了 63.6%和 56.3%,但在随后的两年中这些值又有所增加。另一方面,CB 则逐年稳定地降低这些值。3 年后,5%水平的 CB 将可提取的 CaCl2-Cd 和 Cu 的浓度降低了 53.6%和 66.8%。CB 和 HB 之间的这些差异是由于两种类型的生物炭在土壤中老化方式的不同。在实验室中模拟了老化过程,XPS 结果表明,生物炭的氧化过程在 CB 表面引入了更多的含氧基团(特别是羧基),而 HB 则较少,这导致 CB 中 Cd 和 Cu 的含氧结合位点相应增加。木质素含量是导致两种生物炭氧化程度差异的主要因素。这些结果表明,在污染土壤中,选择合适的生物炭来稳定降低潜在有毒元素(Cd 和 Cu)的生物有效性非常重要。