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首页> 外文期刊>Environmental Pollution >Contrasting impacts of pre- and post-application aging of biochar on the immobilization of Cd in contaminated soils
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Contrasting impacts of pre- and post-application aging of biochar on the immobilization of Cd in contaminated soils

机译:生物炭施用前和施用后老化对污染土壤中镉固定化的影响

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摘要

Biochar has been used for immobilizing heavy metals in soils due to its abundant surface functional groups and mineral components. However, as carbonaceous material, biochar in soils is susceptible to natural aging, which could alter its structural properties and ability to retain heavy metals. In this study, the impacts of pre- and post-application aging on the properties of dairy manure and sawdust biochars and the significance of different mechanisms of complexation with surface functional groups and mineral precipitation for Cd immobilization in soils were investigated. The simulated natural aging including 25 dry-wet cycles and 25 freeze-thaw cycles decreased the pH of biochar from 8.2 to 10.7 to 7.5-9.7 while increased the release of dissolved organic carbon from 4.1 to 10.9 to 5.9-21.3 mg L-1, O/C ratios from 0.09 to 030 to 0.17-033, and O-containing functional groups, especially -OH and -C=O groups. New minerals such as CaC2O4 and MgO center dot MgCO3 were formed during freeze-thaw cycles. The capacity of pre-aged biochars to immobilize Cd in soils decreased from 57-70% to 53-63%, compared to that of fresh biochar, which was mainly due to decrease of CdCO3 or Cd-3(PO4)(2) precipitation as evidenced by XRD and MINTEQ modeling. By contrast, post-aging of biochar application in soil with dry-wet and freeze-thaw cycling had little effect on the biochar's alkalinity while increased the O/C ratios from 0.10 to 0.24 to 0.15-0.27 and intensity of O-containing functional groups. The immobilization capacity of biochars for Cd in soil increased from 44-68% to 59-73% due to the enhanced surface complexation with O-containing groups. In short, biochar subjected to pre-aging had a reduced capacity to immobilize Cd, while biochars with post-aging in soil increased its Cd immobilization capacity as a soil amendment. (C) 2018 Elsevier Ltd. All rights reserved.
机译:由于其丰富的表面官能团和矿物质成分,生物炭已被用于固定土壤中的重金属。然而,作为碳质材料,土壤中的生物炭易受自然老化的影响,这可能会改变其结构特性和保留重金属的能力。在这项研究中,研究了施用前和施用后老化对奶牛粪便和锯末生物炭性质的影响,以及与表面官能团络合的不同机制和矿物沉淀对土壤中Cd固定化的意义。模拟的自然老化过程(包括25个干湿循环和25个冻融循环)将生物炭的pH从8.2降低到10.7到7.5-9.7,同时将溶解有机碳的释放从4.1降低到10.9到5.9-21.3 mg L-1, O / C比为0.09至030至0.17-033,并且含O的官能团,尤其是-OH和-C = O。在冻融循环中形成了新的矿物质,例如CaC2O4和MgO中心点MgCO3。与新鲜生物炭相比,老化生物炭将Cd固定在土壤中的能力从57-70%降低至53-63%,这主要是由于CdCO3或Cd-3(PO4)(2)沉淀的减少XRD和MINTEQ建模证明了这一点。相比之下,通过干湿循环和冻融循环在土壤中施用生物炭后老化对生物炭的碱度影响很小,同时将O / C比从0.10提高至0.24至0.15-0.27,并提高了含O官能团的强度。由于与含O基团的表面络合作用增强,生物炭对土壤中Cd的固定能力从44-68%增加到59-73%。简而言之,经过预老化的生物炭固定化Cd的能力降低,而在土壤中具有后老化的生物炭作为土壤改良剂提高了Cd固定化的能力。 (C)2018 Elsevier Ltd.保留所有权利。

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