Dep. of Renewable Resources, Univ. of Alberta, 442 Earth Sciences Building, Edmonton, AB, T6G 2E3, Canada.
J Environ Qual. 2020 May;49(3):688-699. doi: 10.1002/jeq2.20069. Epub 2020 Mar 20.
Ecosystem reconstruction after mining disturbance is a challenge considering the multitude of factors that affect soil formation and revegetation. In the boreal forest of western Canada, peat material is often used as the organic amendment for land reclamation to upland forest. Carbon and water dynamics of peat-dominated ecosystems differ from natural upland forest soils. The objective of this work was to evaluate the evolution of soils reconstructed after mining disturbance using C and H analyses of n-alkane tracers. Ten soils from natural ecosystems were sampled (0-10 cm) and compared with 11 soils from novel ecosystems ranging in age from 0 to 30 yr, as well as a fresh peat sample. Soils supported different vegetation, including pine (Pinus spp.), aspen (Populus spp.), and white spruce [Picea glauca (Moench) Voss]. Despite overlaps for some individual n-alkanes, we found a dominance of n-C in reconstructed soils, also dominant in the peat material, and a dominance of n-C in natural soils, one of the dominant n-alkanes in natural forest vegetation. In addition, there was a significant difference in odd n-alkane δ H and δ C values between natural and reconstructed soils (p < .05). Differences in δ H values, more negative for reconstructed soils than for natural soils, were attributed to changes in soil moisture, from wetter peat-dominated soils to drier upland forests; among forest types, δ H values were most negative under pine vegetation. The δ C composition of odd n-alkanes, in particular n-C , was significantly related to tree age (p < .05). Overall, both H and C isotopic signatures of odd n-alkanes exhibited differences between natural and reconstructed soils. However, within the reconstructed soils, neither isotopic signature showed a clear evolution with age since reclamation.
采矿干扰后生态系统的重建是一个挑战,因为有许多因素会影响土壤的形成和植被的恢复。在加拿大西部的北方森林,泥炭材料常被用作土地开垦到旱地森林的有机改良剂。泥炭为主的生态系统的碳和水动态与天然旱地森林土壤不同。本工作的目的是通过正构烷烃示踪剂的 C 和 H 分析来评估采矿干扰后重建土壤的演变。从天然生态系统中采集了 10 个土壤样本(0-10 cm),并与 11 个年龄从 0 到 30 年的新型生态系统的土壤样本以及新鲜泥炭样本进行了比较。土壤支持不同的植被,包括松树(Pinus spp.)、白杨(Populus spp.)和白云杉 [Picea glauca(Moench)Voss]。尽管一些个体正构烷烃存在重叠,但我们发现重建土壤中以 n-C 为主,泥炭材料中也以 n-C 为主,而天然土壤中以 n-C 为主,这是天然森林植被中主要的正构烷烃之一。此外,天然土壤和重建土壤之间的奇数正构烷烃的 δ H 和 δ C 值存在显著差异(p < 0.05)。重建土壤的 δ H 值比天然土壤更负,这归因于土壤水分的变化,从更潮湿的泥炭为主的土壤到更干燥的旱地森林;在森林类型中,在松树植被下 δ H 值最负。奇数正构烷烃的 δ C 组成,特别是 n-C,与树木年龄显著相关(p < 0.05)。总的来说,奇数正构烷烃的 H 和 C 同位素特征在天然土壤和重建土壤之间存在差异。然而,在重建土壤中,自开垦以来,这两种同位素特征都没有表现出明显的年龄演变。