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Evaluation of Green Waste and Popular Twigs Biochar Produced at Different Pyrolysis Temperatures for Remediation of Heavy Metals Contaminated Soil

机译:不同热解温度下产生的绿色废弃物和常用枝条生物炭的修复对重金属污染土壤的修复作用

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Remediation of heavy metals contaminated soil through biochar addition depends upon the characteristics of biochar. Feedstock and pyrolysis temperature used for biochar production are the main factors that influence the properties of biochar important for metals immobilization in soil. In this study, immobilization of the most prevalent heavy metals [(lead (Pb (II)), cadmium (Cd) and chromium (Cr)] by green waste and popular twigs biochar produced at different pyrolysis temperatures (low 350°C and high 650°C), has been investigated, following the determination of physical and chemical properties of biochar. Soil was spiked with Pb, Cd and Cr and then amended with different biochar types in an incubation experiment. Soil chemical properties and available concentration of metals were measured at three incubation durations (0, 45 and 90 days). Biochar produced from green waste at 350°C pyrolysis temperature had maximum concentration of oxygen-containing functional groups (0.38 meq g -1 ) and had maximum CEC (43.7 cmol c kg -1 ) as compared with all other biochars. However, fixed carbon content (69.8%) and surface area (309.58 m 2 g -1 ) was found maximum in the biochar produced at 650°C pyrolysis temperature from popular twigs and green waste, respectively. Available concentrations of all three heavy metals were significantly decreased with the passage of time after biochar addition as compared with control and the minimum available concentrations of metals (Pb 6.33 mg kg -1 , Cd 1.42 mg kg -1 and Cr 3.14 mg kg -1 ) were determined in the treatment where green waste biochar produced at 350°C pyrolysis temperature was added to soil after 90 days of incubation duration. Soil chemical properties was significantly improved after biochar addition, especially soil CEC which was found maximum (21.90 cmol c kg -1 ) in the treatment where green waste biochar produced at 350°C pyrolysis temperature was added to soil. We concluded that the addition of green waste biochar produced at low pyrolysis temperature (350°C) to heavy metals contaminated soil showed minimum available concentration of metals due to its better physicochemical characteristics and more oxygen-containing functional groups and by improving the soil chemical properties as compared with other biochars.
机译:通过添加生物炭修复受重金属污染的土壤取决于生物炭的特性。用于生产生物炭的原料和热解温度是影响对金属固定在土壤中重要的生物炭特性的主要因素。在这项研究中,通过在不同的热解温度下(低350°C和高热)生产的绿色废物和流行的树枝生物炭固定最流行的重金属[(铅(Pb(II)),镉(Cd)和铬(Cr)])在确定生物炭的物理和化学特性后,进行了650°C的研究,在土壤中添加了Pb,Cd和Cr,然后在孵化实验中对不同类型的生物炭进行了修正,对土壤化学特性和有效金属含量进行了测定。在三个孵育时间(0、45和90天)进行测量时,在350°C的热解温度下,由绿色废物产生的生物炭具有最大的含氧官能团浓度(0.38 meq g -1)和最大CEC(43.7 cmol c kg) -1),与其他所有生物炭相比,固定温度(69.8%)和表面积(309.58 m 2 g -1)在由普通树枝和绿色废物经650°C热解温度生产的生物炭中最大,分别可用与对照和最低有效金属浓度(Pb 6.33 mg kg -1,Cd 1.42 mg kg -1和Cr 3.14 mg kg -1)相比,添加生物炭后,随着时间的推移,所有三种重金属的浓度均显着降低。在处理90天后,将在350°C热解温度下产生的绿色废物生物炭添加到土壤中的处理方法进行了测定。添加生物炭后,土壤化学性质得到了显着改善,特别是在向土壤中添加了在350°C的热解温度下产生的绿色废物生物炭的处理中,土壤CEC最大(21.90 cmol c kg -1)。我们得出的结论是,在低热解温度(350°C)下向受重金属污染的土壤中添加绿色废物生物炭显示出最低的金属有效浓度,这是由于其更好的理化特性和更多的含氧官能团以及通过改善土壤化学性质与其他生物炭相比。

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