Centre for Advanced Scientific Research (CICA), Faculty of Sciences, University of A Coruna, 15071, A Coruña, Spain.
GEOBIOTEC, Geosciences Department, Aveiro University, Campus de Santiago, 3810-193, Aveiro, Portugal.
Environ Geochem Health. 2018 Oct;40(5):1803-1815. doi: 10.1007/s10653-017-9940-7. Epub 2017 Mar 24.
This study aims to determine aluminum fractions in the fine earth of acidic soils under different land uses (forest, pasture and cultivation) and in the river bed sediments of the headwater of the Mero River in order to identify and quantify Al-bearing phases to assess Al mobility and potential bioavailability (environmental availability) in the monitoring area. Sequential extraction is used to evaluate the Al partitioning into six fractions operationally defined: soluble/exchangeable/specifically adsorbed, bound to manganese oxides, associated with amorphous compounds, aluminum bound to oxidizable organic matter, associated with crystalline iron oxides, and residual fraction (aluminum within the crystal lattices of minerals). The mean concentration of total aluminum (24.01 g kg) was similar for the three considered uses. The mean percentage of the aluminum fractions, both in soils and sediments, showed the following order: residual fraction ≫ amorphous compounds ≈ crystalline iron oxides > water-soluble/exchangeable/specifically adsorbed > bound to oxidizable organic matter ≈ Mn oxides. However, in the soils, the amorphous compounds and water-soluble/exchangeable/specifically adsorbed fraction showed considerable differences between some types of uses, the percentage of aluminum linked to amorphous compounds being higher in forest soils (16% of total Al) compared to other uses (mean about 8% of total Al). The highest values of water-soluble/exchangeable/specifically adsorbed Al were also found in forest soils (mean 8.6% of the total Al versus about 4% of pasture and cultivation), which is consistent with the lower pH and higher organic matter content in forest soils. Nevertheless, the potentially bioavailable fraction (sum of the first three fractions) is low, suggesting very low geoavailability of this element in both soils and sediments; hence, the possibility to affect the crops and water quality is minimal.
本研究旨在确定不同土地利用方式(森林、草地和耕地)下酸性土壤细土以及梅罗河源头河床沉积物中的铝形态,以识别和量化含铝相,评估监测区域中铝的迁移性和潜在生物可利用性(环境可利用性)。采用连续提取法评估 Al 按 6 种形态分配:可溶/可交换/专性吸附、与锰氧化物结合、与无定形化合物结合、与氧化有机物质结合、与结晶氧化铁结合和残留态(矿物晶格内的铝)。三种考虑用途的总铝平均浓度(24.01 g kg)相似。土壤和沉积物中各铝形态的平均百分率呈现如下顺序:残留态≫无定形化合物≈结晶氧化铁>水溶性/可交换/专性吸附>与氧化有机物质结合≈Mn 氧化物。然而,在土壤中,无定形化合物和水溶性/可交换/专性吸附相在某些用途之间存在明显差异,与其他用途(总 Al 的平均约 8%)相比,与无定形化合物结合的铝百分比在森林土壤中更高(总 Al 的 16%)。水溶性/可交换/专性吸附 Al 的最高值也出现在森林土壤中(总 Al 的平均值为 8.6%,而草地和耕地约为 4%),这与森林土壤中较低的 pH 值和较高的有机质含量一致。然而,潜在生物可利用的分数(前三个分数的总和)较低,表明该元素在土壤和沉积物中的地球化学可用性非常低;因此,对作物和水质产生影响的可能性很小。