Instituto de Recursos Naturales y Agrobiología de Sevilla, CSIC, PO Box 1052, 41080 Sevilla, Spain.
Environ Pollut. 2011 Oct;159(10):3018-27. doi: 10.1016/j.envpol.2011.04.015. Epub 2011 May 10.
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.
我们研究了各种副产品(糖甜菜石灰、生物固体堆肥和风化煤)的效率,这些副产品基于单一或重复应用于田间试验,以建立与稳定策略兼容的植被覆盖,该稳定策略针对的是初始改良应用后 4-6 年的多元素(As、Cd、Cu、Pb 和 Zn)污染土壤。结果表明,再处理的需求取决于改良剂和元素;在某些情况下,单一应用可能会降低地上生物量中的痕量元素浓度,并促进健康植被覆盖的建立。通过覆盖百分比、生物量和定殖分类群数量来评估改良剂性能有所不同;然而,植物群落组成的变化不一定是改良剂特有的。尽管向植物生物区系转移的痕量元素在重新植被区域中更大,但由于土壤侵蚀和植物吸收,总体上痕量元素的损失通常小于裸土。