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Fractionation of Cd, Cu, Ni, Pb, and Zn in floodplain soils from Egypt, Germany and Greece

机译:CD,Cu,Ni,Pb和Zn中的埃及,德国和希腊的洪泛区土壤分级

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Trace elements are potentially toxic to human life and the environment. Element toxicity depends on chemical associations in soils. Therefore, determining the chemical form of an element in soils is important to evaluate its mobility and bioavailability. Initial soil development in river floodplains influences soil properties, processes and therefore behavior of trace elements. In this study, three different floodplain soils sampled at three rivers (Nile/Egypt, Elbe/Germany and Penios/Greece) were used to link soil development and properties to the geochemical fractions and mobility of some trace elements. Sequential extraction was used to fractionate five trace elements (Cd, Cu, Ni, Pb and Zn) into five operationally defined groups: water soluble + exchangeable, carbonate, Fe-Mn oxide, organic, and residual. German soil showed the highest total concentration of the studied elements (except Ni). The Greek soil had the greatest amount of Ni. The residual fraction was the abundant pool for the studied elements examined in the Egyptian and Greek soils while the non-residual fraction was the dominant pool for all elements in the German soil. A significant amount (71- 94%) of all elements was present in German soil in the potentially available fraction: non-residual fraction, while the amount of this fraction ranged between 9 and 39 % in Greek soil and between 9 and 34 % in Egyptian soil. These suggest that the potential availability of the studied trace elements was extremely high in German soil compared to the Egyptian and Greek soil. In the German soil, most of the non-residual Cd, Ni and Zn were bounded with the Fe-Mn oxide fraction, while Cu and Pb distributed in the organic fraction. While in the Egyptian and Greek soils Fe-Mn oxide fraction was the abundant pool for the studied elements except for Cd, in which the exchangeable and the carbonate fractions had the greatest amount of Cd. Assuming that mobility and bioavailability of these elements are related to their solubility and geochemical forms, and that they decrease in the order of extraction sequence, the apparent mobility and potential bioavailability for the studied elements in the soils were: Cu > Cd > Ni > Pb = Zn in Egyptian soil, Cd > Cu > Pb> Ni = Zn in Greek soil and Cd > Zn> Pb> Cu > Ni in German soil.
机译:微量元素对人类生活和环境有潜在毒性。元素的毒性取决于土壤化学协会。因此,在确定土壤中的元素的化学形式是重要的,以评估其流动性和生物利用度。在河流土壤初始发展漫滩影响土壤性质,过程,因此微量元素的行为。在这项研究中,三个不同的漫滩土壤在三条河(尼罗河/埃及,易北河/德国和Penios /希腊)被用来链接土壤发育和属性地球化学组分和移动某些微量元素的采样。连续提取物用于分级分离5种微量元素(镉,铜,镍,铅和锌)成五个操作上定义的组:水溶性+可交换,碳酸盐,铁锰氧化物,有机和残差。德国土壤表明所研究的元素(除Ni)的最高总浓度。希腊土壤由于Ni量最大。剩余的部分是在埃及和希腊的土壤检验所研究的内容丰富的池而非残留量是在德国的土地所有元素占主导地位的游泳池。所有元件的显著量(71- 94%)存在于潜在可用分数德语土壤:非残余馏分,而这部分的量在范围在希腊语土壤9和39%之间和9和34%之间埃及领土。这些表明,所研究的微量元素的潜在供应量在德国的土地极高相比,埃及和希腊的土壤。在德国土壤,大部分的非残留镉,Ni和Zn的与所述铁锰氧化物级分界,而Cu和Pb分布在有机部分。而在埃及和希腊土壤铁锰氧化物分数是丰富池除了Cd中的研究的元件,其中所述可更换和碳酸酯组分有镉的量最大。假设这些元素的移动性和生物利用度都与它们的溶解度和地球化学的形式,并且它们在提取序列的顺序降低,表观流动性和潜在的生物利用度为在土壤中所研究的元素是:铜>镉>镍>铅=锌在埃及土壤,镉>铜>铅>镍锌=希腊土壤镉>锌>铅>铜>镍在德国的土地。

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