Institute of Soil and Water Resources and Environmental Science, Zhejiang Provincial Key Laboratory of Agricultural Resources and Environment, Zhejiang University, Hangzhou 310058, China.
Institute of Soil and Water Resources and Environmental Science, Zhejiang Provincial Key Laboratory of Agricultural Resources and Environment, Zhejiang University, Hangzhou 310058, China.
Sci Total Environ. 2018 Aug 15;633:300-307. doi: 10.1016/j.scitotenv.2018.03.199. Epub 2018 Mar 22.
Biochar has been utilized as a good amendment to immobilize heavy metals in contaminated soils. However, the effectiveness of biochar in metal immobilization depends on biochar properties and metal species. In this study, the biochars produced from co-pyrolysis of rice straw with swine manure at 400°C were investigated to evaluate their effects on bioavailability and chemical speciation of four heavy metals (Cd, Cu, Pb and Zn) in a Pb-Zn contaminated soil through incubation experiment. Results showed that co-pyrolysis process significantly change the yield, ash content, pH, and electrical conductivity (EC) of the blended biochars compared with the single straw/manure biochar. The addition of these biochars significantly increased the soil pH, EC, and dissolved organic carbon (DOC) concentrations. The addition of biochars at a rate of 3% significantly reduced the CaCl-extractable metal concentrations in the order of Pb>Cu>Zn>Cd. The exchangeable heavy metals decreased in all the biochar-amended soils whereas the carbonate-bound metal speciation increased. The increase in soil pH and the decrease in the CaCl extractable metals indicated that these amendments can directly transform the highly availability metal speciation to the stable speciation in soils. In conclusion, biochar derived from co-pyrolysis of rice straw with swine manure at a mass ratio of 3:1 could most effectively immobilize the heavy metals in the soil.
生物炭已被用作固定污染土壤中重金属的良好改良剂。然而,生物炭在重金属固定中的有效性取决于生物炭特性和金属种类。在这项研究中,通过培养实验研究了在 400°C 下由稻草与猪粪共热解产生的生物炭对 Pb-Zn 污染土壤中四种重金属(Cd、Cu、Pb 和 Zn)生物可利用性和化学形态的影响。结果表明,与单一的稻草/粪便生物炭相比,共热解过程显著改变了混合生物炭的产率、灰分含量、pH 值和电导率(EC)。这些生物炭的添加显著增加了土壤的 pH 值、EC 和溶解有机碳(DOC)浓度。以 3%的添加率添加生物炭可显著降低 CaCl 提取的金属浓度,顺序为 Pb>Cu>Zn>Cd。所有添加生物炭的土壤中可交换的重金属减少,而碳酸盐结合的金属形态增加。土壤 pH 值的升高和 CaCl 提取金属的减少表明这些改良剂可以直接将高生物有效性的金属形态转化为土壤中的稳定形态。总之,以质量比 3:1 由稻草和猪粪共热解得到的生物炭可以最有效地固定土壤中的重金属。