Geological Survey of Norway, P.O. Box 6315, Torgarden, N-7491 Trondheim, Norway.
Geological Survey of Norway, P.O. Box 6315, Torgarden, N-7491 Trondheim, Norway.
Sci Total Environ. 2019 Feb 15;651(Pt 1):1344-1355. doi: 10.1016/j.scitotenv.2018.09.272. Epub 2018 Sep 22.
Eight regional to continental scale datasets providing Cd concentrations in subsoil (C horizon or mineral soil collected at depth) and topsoil are used to compare the statistical distribution of Cd in the two soil layers. Topsoil is invariably enriched in Cd when compared to subsoil. When both horizons are mineral soil the concentration ratio Cd/Cd is 1.3-2.2. This ratio is substantially larger (6.6-16.5) when mineral subsoil is compared to an organic topsoil O horizon. Data from regional multi-media transects underline that Cd, despite of toxicity, plays an important role in the biosphere, and several plants and a mushroom not only accumulate but also adjust their Cd content. Because organic topsoil is derived from local vegetation residues, its Cd cumulative distribution function (CDF) reflects also Cd accumulation related to local plant diversity. This is a major difference to Pb which is not usually actively taken up by plants, whereby a linear concentration shift between mineral soil and organic soil dominates the CDFs. To estimate the amount of excess Cd due to diffuse contamination, the low-concentration ends of the CDFs from the regional datasets are studied. For two datasets a diffuse Cd contamination below 0.03 mg/kg emerges, a reasonable value when compared to either the median concentration of 0.15 mg/kg Cd in topsoil, or to published Cd fluxes. For the other datasets the apparent diffuse Cd input is between 0.05 and 0.28 mg/kg. In one data set this seems to indicate a true contamination blanket due to several large-scale regional anthropogenic sources at the single country scale. In many surveys, the low end of the subsoil Cd concentration is difficult to assess due to analytical limitations. The results suggest that hitherto neglected natural processes selectively accumulate Cd and substantially change its distribution characteristics in the biosphere and the organic topsoil.
使用 8 个区域性到大陆性尺度的数据集,这些数据集提供了表土(C 层或在深度处采集的矿物质土壤)和底土中 Cd 浓度,用于比较这两个土壤层中 Cd 的统计分布。与底土相比,表土总是富含 Cd。当两个土层都是矿物质土壤时,Cd/Cd 的浓度比为 1.3-2.2。当矿物质底土与有机表土 O 层相比时,该比值显著更大(6.6-16.5)。来自区域多介质横截面上的数据强调了 Cd 的重要性,尽管 Cd 具有毒性,但它在生物圈中发挥着重要作用,一些植物和蘑菇不仅积累 Cd,而且还调整它们的 Cd 含量。由于有机表土是由当地植被残渣衍生而来的,其 Cd 累积分布函数(CDF)也反映了与当地植物多样性相关的 Cd 积累。这与 Pb 形成了主要区别,Pb 通常不会被植物主动吸收,因此矿物质土壤和有机土壤之间的线性浓度变化主导了 CDF。为了估计由于扩散污染而导致的过量 Cd 量,研究了来自区域数据集的 CDF 的低浓度端。对于两个数据集,发现存在低于 0.03 mg/kg 的扩散 Cd 污染,这是一个合理的值,与表土中 0.15 mg/kg Cd 的中位数浓度或已发表的 Cd 通量相比都是如此。对于其他数据集,表观扩散 Cd 输入介于 0.05 和 0.28 mg/kg 之间。在一个数据集中,这似乎表明由于在单个国家范围内存在几个大规模的区域人为源,存在真正的污染覆盖层。在许多调查中,由于分析限制,底土 Cd 浓度的低端难以评估。结果表明,迄今被忽视的自然过程选择性地积累 Cd,并在生物圈和有机表土中大大改变了其分布特征。