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Phytostabilization of semiarid soils residually contaminated with trace elements using by-products: sustainability and risks

机译:使用副产品对残留有微量元素的半干旱土壤进行植物稳定化:可持续性和风险

摘要

We investigated the efficiency of various by-products (sugarbeet lime, biosolid compost and leonardite), based on single or repeated applications to field plots, on the establishment of a vegetation cover compatible with a stabilization strategy on a multi-element (As, Cd, Cu, Pb and Zn) contaminated soil 4-6 years after initial amendment applications. Results indicate that the need for re-treatment is amendment- and element-dependent; in some cases, a single application may reduce trace element concentrations in above-ground biomass and enhance the establishment of a healthy vegetation cover. Amendment performance as evaluated by % cover, biomass and number of colonizing taxa differs; however, changes in plant community composition are not necessarily amendment-specific. Although the translocation of trace elements to the plant biotic compartment is greater in re-vegetated areas, overall loss of trace elements due to soil erosion and plant uptake is usually smaller compared to that in bare soil.
机译:我们基于对田间地块的单次或重复施用,在建立了与多元素稳定化策略兼容的植被覆盖物(砷,镉,磷和镉)的基础上,研究了各种副产物(甜菜石灰,生物固体堆肥和变绿石)的效率。初次施用改良剂4-6年后,土壤中的Cu,Pb和Zn被污染)。结果表明,重新治疗的需要依赖于修正和元素。在某些情况下,一次施用可能会降低地上生物量中的微量元素浓度,并增强健康植被的覆盖范围。根据覆盖率,生物量和定殖类群数量评估的修正性能不同;但是,植物群落组成的变化不一定是针对特定修正案的。尽管在重新植被的地区中微量元素向植物生物区系的转移更大,但与裸土相比,由于土壤侵蚀和植物吸收而导致的微量元素总体损失通常较小。

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