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首页> 外文期刊>Applied Geochemistry: Journal of the International Association of Geochemistry and Cosmochemistry >Comparison of Pb stabilization in a contaminated calcareous soil by application of vermicompost and sheep manure and their biochars produced at two temperatures
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Comparison of Pb stabilization in a contaminated calcareous soil by application of vermicompost and sheep manure and their biochars produced at two temperatures

机译:用蠕虫和绵羊粪便及其两种温度产生的羊毛粪肥污染钙质土壤Pb稳定化比较

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Soil contamination with potentially toxic elements (PTEs) is increasing due to human activities including the widespread use of chemical fertilizers, sludge and industrial wastewater in agriculture. In situ stabilization of soil PTEs using organic amendments is a cost effective and efficacious method. A laboratory experiment was conducted to investigate the effect of two organic materials (sheep manure (SM) and vermicompost (VC)) and their biochars (SMB and VCB) produced at two pyrolysis temperatures (300 and 500 degrees C) at 2 wt. % on Pb immobilization in a contaminated calcareous soil. A sequential extraction procedure, mobility factor and release kinetics were used for evaluating efficiency of the amendments. Addition of the biochars resulted in a significant decrease in exchangeable (10.4-19.6%) and carbonate (3.8-10.5%) forms of soil Pb, while Pb bound to amorphous Fe oxides (4.3-52.9%) was increased. The application of VCB produced at 500 degrees C resulted in the greatest mobility factor reduction (11%), likely due to its characteristics such as high pH (10.5), high P (0.39%) and ash content (67.7%). Two first-order reactions model best fitted the Pb release data extracted by EDTA, indicating Pb release took place from two sections of the soil with different adsorption and solubility properties. The lowest amount of Pb extracted in Q(1) and Q(2) phases were observed in VCB (115.2 mg kg(-1)) and SMB (105.5 mg kg(-1)) produced at 500 degrees C treatments, respectively. Generally, the effect of biochars produced at higher temperature (500 degrees C) on the soil Pb stabilization was greater than those produced at lower temperature (300 degrees C), while the feedstocks (SM and VC) had no significant effect in stabilizing soil Pb.
机译:由于人类活动,具有潜在有毒元素(PTES)的土壤污染,包括普遍使用的农业化学肥料,污泥和工业废水。使用有机修改的土壤ptes原位稳定是一种成本效益和有效的方法。进行实验室实验以研究两种有机物质(SM)和蛭数(VC))的效果及其在2重量%的热解温度(300和500℃)下产生的生物脉冲(SMB和VCB)。污染钙质土壤中Pb固定的%。连续提取程序,移动因子和释放动力学用于评估修正的效率。添加生物触盘导致可交换(10.4-19.6%)和碳酸盐(3.8-10.5%)的土壤pb的显着降低,而Pb与无定形Fe氧化物结合(4.3-52.9%)。在500℃下产生的VCB施加导致最大的迁移率因数减少(11%),可能是由于其特性,例如高pH(10.5),高p(0.39%)和灰分(67.7%)。两次一级反应模型最能拟合EDTA提取的PB释放数据,表明Pb释放从具有不同吸附和溶解性的土壤的两部分发生。在Q(1)和Q(2)相中提取的最低量的Pb在VCB(115.2mg kg(-1))和SMB(105.5mg kg(-1))分别以500℃治疗产生。通常,在较高温度(500摄氏度)上产生的生物脉冲的效果大于在较低温度(300℃)下产生的生物脉冲的影响,而原料(SM和VC)在稳定土壤PB方面没有显着影响。

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