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Effects of softwood biochar on the status of nitrogen species and elements of potential toxicity in soils

机译:软木生物炭对土壤氮素状况和潜在毒性元素的影响

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The effects of softwood-derived biochar materials on the chemical behaviour of environmental contaminants in soils were examined in two microcosm scenarios. Addition of the biochar materials into an alkaline sandy soil significantly reduced NH3 volatilization and made it available for conversion into NO3 via nitrification. This process could be enhanced by an increased application rate of biochar produced at a higher pyrolysis temperature. Under the alkaline conditions encountered in the experiment, the biochar surfaces tended to be negatively charged which disfavours the adsorption of NO3-. Therefore, in a fully open system, the addition of biochar materials was likely to contribute to nitrate leaching from the fertilized alkaline sandy soil. The effects of the biochar materials on the immobilization of Fe2+ generated via anaerobic iron reduction in the inundated contaminated soil were not observed, except for the treatment with a higher dose of biochar material produced under pyrolysis temperature at 700 degrees C after the 240th h of incubation. Arsenic showed similar behaviour to Fe. Zn tended to have a higher affinity to the biochar, as compared to Mn. Immobilization of Pb occurred regardless of whether or not the biochar is present.
机译:在两个微观场景中,考察了针叶木生物炭材料对土壤中环境污染物化学行为的影响。将生物炭材料添加到碱性沙质土壤中可显着减少NH3的挥发,并使其可通过硝化转化为NO3。在较高的热解温度下,通过增加生物炭的施用率可以增强该过程。在实验中遇到的碱性条件下,生物炭表面趋于带负电,这不利于NO3-的吸附。因此,在完全开放的系统中,生物炭材料的添加可能有助于硝酸盐从施肥的碱性砂土中浸出。未观察到生物炭材料对通过厌氧铁还原而产生的Fe2 +固定在被淹没的污染土壤中的影响,除了在240孵育小时后在700摄氏度的热解温度下用较高剂量的生物炭材料处理之外。 。砷表现出与铁相似的行为。与Mn相比,Zn倾向于对生物炭具有更高的亲和力。不管是否存在生物炭,都会发生铅的固定化。

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