生物炭与沸石复配对碱性土壤铅镉有效性的影响

Effects of Biochar and its Mixture of Zeolite on Availability of Lead and Cadmium in Alkaline Soil

  • 摘要:
      目的  以生物炭单施及其与沸石复配为钝化剂,研究其对铅镉复合污染碱性土壤理化性质及铅镉有效性的影响,以期用钝化技术为碱性土壤重金属污染原位修复提供理论和实践支持。
      方法  以河南某金属冶炼厂附近铅(Pb)镉(Cd)污染的碱性菜地土壤(Pb 227.75 mg kg−1、Cd 3.38 mg kg−1)为研究对象,采用盆栽试验,研究生物炭单施及其与沸石复配(生物炭∶沸石 = 1∶1)不同施入量(0、1%、2.5%、5%)对土壤理化性质、土壤Pb、Cd有效态含量、青菜根和叶中Pb、Cd含量以及青菜富集转运Pb、Cd的影响。
      结果  与对照相比,生物炭单施及其与沸石复配处理,使土壤pH提高了0.03 ~ 0.17个单位,与对照无显著差异,但显著提高了土壤有机质、碱解氮、有效磷和速效钾含量(P < 0.05)。土壤有效态Pb、Cd含量随钝化剂施用量增加呈下降趋势,分别下降了10.69% ~ 32.75%和7.63% ~ 26.72%,相同施用量下复配处理效果优于单施处理。生物炭及其复配沸石促进了青菜生长,降低了青菜Pb的含量,根部和茎叶中Pb的含量比对照分别下降了2.79% ~ 64.90%和4.76% ~ 76.19%,5%施入量下降作用显著(P < 0.05),对青菜根部Cd含量也有降低作用,但没能降低茎叶中Cd的含量,Cd在青菜中有较高的富集和转运能力。相关分析表明,青菜Pb、Cd含量受pH变化影响较小,与土壤有机质含量显著相关(P < 0.05)。
      结论  在铅镉复合污染碱性土壤中,生物炭及其与沸石复配都改变了土壤理化性质,与单施生物炭相比,复配处理降低土壤铅镉有效性作用较大,铅镉有效性受土壤pH变化影响较小,但受有机质含量影响较大,青菜对土壤中镉的富集和转运能力高于铅。

     

    Abstract:
      Objective  In order to provide a theoretical basis for the in-situ remediation on lead (Pb)- cadmium (Cd) contaminated alkaline soil, biochar and its mixture of zeolite were used as passivating agents to study their effects on the physical and chemical properties and the availability of Pb and Cd in soil.
      Method  Using Cd-Pb contaminated soils (Pb 227.75 mg kg−1, Cd 3.38 mg kg−1) collected from vegetable fields near the metal smelter in Henan Province, pot culture experiments were conducted to evaluate the effects of different amounts of biochar (0, 1%, 2.5%, and 5%) and its mixture of zeolite (biochar∶zeolite = 1∶1) on the soil physical and chemical properties, the concentration of available Pb and Cd in the tested soil, and accumulation and translocation of Cd and Pb in the green vegetable.
      Result  Compared with the control treatment, the application of biochar and its mixture of zeolite increased soil pH by 0.03 - 0.17 and increased significantly the contents of soil organic matter, alkali-hydrolyzed nitrogen, available phosphorus, and potassium (P < 0.05). The concentrations of available Pb and Cd in the soil decreased by 10.69% - 32.75% and 7.63% - 26.72% with the increase of amendment agents. The effect of the mixture agents was greater than that of the biochar under the same application amount. The passivating agents promoted green vegetable growth and reduced the accumulation of Pb in the green vegetables. The contents of Pb in the root, stem and leaf decreased by 2.79% - 64.90% and 4.76% - 76.19%, respectively. And there was a significant decrease when the amount of passivating agent was 5% (P < 0.05). The agents also reduced the contents of Cd in the root, but they failed to reduce those in the stem and leaf. The accumulation and translocation capacity of green vegetable was greater for Cd than that for Pb. A related analysis showed that the availabilities of Pb and Cd in green vegetables were less affected by pH changes, but they were significantly and negatively associated with the soil organic matter content (P < 0.05).
      Conclusion  In Pb-Cd contaminated alkaline soil, the biochar and its compound of zeolite both changed soil's physical and chemical properties. Compared with the application of biochar, the compound treatment played the more role in reducing the effectiveness of soil Pb and Cd in the soil. The availabilities of Pb and Cd were less affected by soil pH change, but greatly affected by organic matter content. There existed a higher accumulation and translocation capacity of Cd than that of Pb in the green vegetables.

     

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