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首页> 外文期刊>The Science of the Total Environment >Sequential extraction of nickel and zinc in sewage sludge- or biochar/sewage sludge-amended soil
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Sequential extraction of nickel and zinc in sewage sludge- or biochar/sewage sludge-amended soil

机译:依次提取污水污泥或生物炭/污水污泥改良土壤中的镍和锌

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Fractionation of nickel (Ni) and zinc (Zn) in sewage sludge-amended soil and in sewage sludge/biochar-amended soil was investigated. The results were compared with ecotoxicological tests in order to determine the contribution of metals to the toxicity of amended soils. The study was conducted as a long-term field experiment. Sewage sludge (SL) or sewage sludge with a 2.5, 5 or 10% addition of biochar (BC) was added to the soil. Samples for analysis were taken immediately after experiment establishment as well as after 12 and 18 months from the beginning of the study. The fractionation analysis of Ni and Zn was performed using the BCR (Community Bureau of Reference) three-step sequential extraction procedure. The following forms were determined: mobile (F1); bound to FeMn oxides (F2); bound to organic matter (F3) and residual (F4). The soil, SL and BC differed in the contribution of individual forms of the metals. The application of SL into the soil resulted in an increased soil content of mobile forms of Ni and Zn by 180 and 103%, respectively. The mobility index (MI) significantly increased, which evidences the risk related to the presence of these metals. Biochar in the sewage sludge significantly reduced the content of Ni and Zn in F1 fraction. The study also demonstrated that biochar amendment promotes the transition over time of available forms of Ni and Zn into their residual forms (F4), which leads to a further reduction in the environmental risk related to their presence in the environment. The conducted statistical analysis revealed only intermittent relationships between the individual forms of the metals and soil physicochemical properties and toxicity, which may indicate more complex mechanisms that occur in the experimental systems investigated. Therefore, the use of SL in combination with BC can be an effective method for reducing the environmental risk related to the presence of metals in SL.
机译:研究了污水污泥改良土壤和污水污泥/生物炭改良土壤中镍(Ni)和锌(Zn)的分离。将结果与生态毒理测试进行比较,以确定金属对改良土壤毒性的贡献。该研究是一项长期的野外实验。向土壤中添加了2.5、5%或10%的生物炭(BC)的污水污泥(SL)或污水污泥。实验建立后以及研究开始后的12和18个月后立即取样进行分析。 Ni和Zn的分馏分析是使用BCR(社区参考局)三步顺序萃取程序进行的。确定了以下形式:移动(F1);与FeMn氧化物(F2)结合;与有机物(F3)和残留物(F4)结合。土壤,SL和BC的金属形态各不相同。将SL施用到土壤中后,可移动形式的Ni和Zn的土壤含量分别增加了180%和103%。迁移率指数(MI)显着提高,这证明了与这些金属的存在有关的风险。污水污泥中的生物碳显着降低了F1馏分中的Ni和Zn含量。这项研究还表明,生物炭改良剂会随着时间的推移促进将可用形式的镍和锌转变为残留形式(F4),从而进一步降低与其在环境中的存在有关的环境风险。进行的统计分析表明,各种形式的金属与土壤理化性质和毒性之间仅存在间歇性关系,这可能表明在所研究的实验系统中发生了更为复杂的机制。因此,将SL与BC结合使用可以降低与SL中金属的存在有关的环境风险,是一种有效的方法。

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