Departamento de Ciencia y Tecnología Agraria, Área de Edafología y Química Agrícola, E.T.S. de Ingeniería Agronómica, Universidad Politécnica de Cartagena, Paseo Alfonso XIII, 48, Cartagena, 30203 Murcia, Spain.
Departamento de Ciencia y Tecnología Agraria, Área de Edafología y Química Agrícola, E.T.S. de Ingeniería Agronómica, Universidad Politécnica de Cartagena, Paseo Alfonso XIII, 48, Cartagena, 30203 Murcia, Spain.
Chemosphere. 2013 Mar;90(10):2512-9. doi: 10.1016/j.chemosphere.2012.10.083. Epub 2012 Nov 16.
The aim of this study was to assess the effectiveness of combining liming and vegetation for the phytomanagement of strongly acidic, saline eutrophic wetlands polluted by mine wastes. Simulated soil profiles were constructed and four treatments were assayed: without liming+without plant, without liming+with plant, with liming+without plant and with liming+with plant. The plant species was the halophyte Sarcocornia fruticosa. Three horizons were differentiated: A (never under water), C1 (alternating flooding-drying conditions) and C2 (always under water). The soluble Cd, Cu, Mn, Pb and Zn concentrations were measured regularly for 18 weeks and a sequential extraction procedure was applied at the end of the experiment. Liming was effective (between ∼70% and ∼100%) in reducing the soluble Zn, Cu and Pb. In contrast, soluble Mn and Cd increased with liming, especially in the treatment with liming+with plant, where the concentrations were 2-fold higher than in the non-limed treatments. The amendment increased the contents of Zn, Mn and Cd bound to potentially-mobilisable soil fractions at the expense of the most-environmentally-inert fractions. Hence, the combined use of liming and vegetation may increase the long-term environmental risk of metals solubilisation.
本研究旨在评估石灰和植被相结合对受矿山废物污染的强酸性、盐沼富营养湿地进行植物修复的效果。模拟土壤剖面,并进行了四种处理:不施石灰+无植物、不施石灰+有植物、施石灰+无植物和施石灰+有植物。植物物种为盐生植物盐角草。区分了三个层次:A(从未浸水)、C1(干湿交替条件)和 C2(始终浸水)。定期测量了 18 周内的可溶性 Cd、Cu、Mn、Pb 和 Zn 浓度,并在实验结束时应用了连续提取程序。石灰处理(70%至 100%之间)有效降低了可溶性 Zn、Cu 和 Pb 的浓度。相比之下,施石灰会增加 Mn 和 Cd 的可溶性,尤其是在施石灰+有植物的处理中,其浓度比未施石灰的处理高两倍。该改良剂增加了潜在可移动土壤部分中 Zn、Mn 和 Cd 的含量,而牺牲了最惰性的部分。因此,石灰和植被的联合使用可能会增加金属溶解的长期环境风险。