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有机物和盐分改变土壤中镉的(植物)有效性。

Organic matter and salinity modify cadmium soil (phyto)availability.

机构信息

University of Zagreb Faculty of Agriculture, Department of Soil Amelioration, Svetosimunska 2510000 Zagreb, Croatia.

University of Zagreb Faculty of Agriculture, Department of Soil Amelioration, Svetosimunska 2510000 Zagreb, Croatia.

出版信息

Ecotoxicol Environ Saf. 2018 Jan;147:824-831. doi: 10.1016/j.ecoenv.2017.09.041. Epub 2017 Sep 26.

Abstract

Although Cd availability depends on its total concentration in soil, it is ultimately defined by the processes which control its mobility, transformations and soil solution speciation. Cd mobility between different soil fractions can be significantly affected by certain pedovariables such as soil organic matter (SOM; over formation of metal-organic complexes) and/or soil salinity (over formation of metal-inorganic complexes). Phytoavailable Cd fraction may be described as the proportion of the available Cd in soil which is actually accessible by roots and available for plant uptake. Therefore, in a greenhouse pot experiment Cd availability was observed in the rhizosphere of faba bean exposed to different levels of SOM, NaCl salinity (50 and 100mM) and Cd contamination (5 and 10mgkg). Cd availability in soil does not linearly follow its total concentration. Still, increasing soil Cd concentration may lead to increased Cd phytoavailability if the proportion of Cd pool in soil solution is enhanced. Reduced Cd (phyto)availability by raised SOM was found, along with increased proportion of Cd-DOC complexes in soil solution. Data suggest decreased Cd soil (phyto)availability with the application of salts. NaCl salinity affected Cd speciation in soil solution by promoting the formation of CdCl complexes. Results possibly suggest that increased Cd mobility in soil does not result in its increased availability if soil adsorption capacity for Cd has not been exceeded. Accordingly, chloro-complex possibly operated just as a Cd carrier between different soil fractions and resulted only in transfer between solid phases and not in increased (phyto)availability.

摘要

尽管镉的可用性取决于其在土壤中的总浓度,但最终还是由控制其迁移、转化和土壤溶液形态的过程决定的。不同土壤组分之间的镉迁移能力可能会受到某些土壤变量的显著影响,如土壤有机质(SOM;形成金属-有机配合物)和/或土壤盐分(形成金属-无机配合物)。可利用的镉部分可以描述为土壤中可利用的镉中实际上可被根系吸收并可被植物吸收的部分。因此,在温室盆栽试验中,研究了暴露于不同 SOM 水平、NaCl 盐度(50 和 100mM)和 Cd 污染(5 和 10mgkg)的蚕豆根际的 Cd 可用性。土壤中 Cd 的可用性并不与其总浓度呈线性关系。然而,如果土壤溶液中 Cd 库的比例增加,土壤中 Cd 浓度的增加可能会导致 Cd 植物可利用性的增加。结果发现,随着 SOM 的增加,Cd 的生物有效性降低,土壤溶液中 Cd-DOC 配合物的比例增加。数据表明,盐分的应用降低了 Cd 的土壤(植物)生物有效性。NaCl 盐度通过促进 CdCl 配合物的形成影响土壤溶液中 Cd 的形态。结果表明,如果土壤对 Cd 的吸附能力没有超过,土壤中 Cd 的迁移增加并不一定会导致其可用性增加。因此,氯配合物可能只是不同土壤组分之间的 Cd 载体,只会导致固相间的转移,而不会增加(植物)可用性。

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