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Post-reclamation land use effects on properties and carbon sequestration in minesoils of southeastern Ohio

机译:垦区后土地利用对俄亥俄东南部矿山土壤的特性和固碳的影响

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Reclamation of mined soils could restore soil quality and ecosystem productivity and sequester C, but limited data exist with regard to the impact of post-reclamation land use and management on soil organic carbon (SOC) storage in reclaimed minesoils (RMS). A study was conducted to evaluate SOC and total nitrogen (TN) stocks (0-50 cm depth) and related soil physical and chemical properties for reclaimed grassland sites maintained under four distinct management practices for 24 years, namely, meadow, hay, grazing, and grazing-feeding. A nearby undisturbed grassland was used as a baseline or reference. Bulk density of the RMS (range: 1.16-1.88 mg m-3) was significantly lower for the hay and meadow than the grazed sites (P < 0.05). In addition, RMS under hay and meadow practices had greater concentration of water-stable aggregates (WSA) and larger mean weight diameter (MWD) of aggregates than the grazed sites. Soil pH and electrical conductivity (EC) were higher in the RMS than the undisturbed soils. Among the reclaimed sites, pH and EC values were generally lower (P < 0.05) in meadow than grazing and grazing-feeding practices. The SOC was generally higher in the grazing-feeding and hay sites (89 and 76 mg ha-1, respectively) than meadow (64 mg ha-1), grazing (70 mg ha-1), and undisturbed grassland (72 mg ha-1). The data suggest that removal of aboveground biomass for hay had no impact on SOC accumulation in these grasslands. Nearly 50% of the root biomass accumulated in the top 0-10 cm in the reclaimed grassland sites. The SOC content was strongly correlated with MWD (R2 = 0.70, P < 0.01), and root biomass (R2 = 0.75 P < 0.01) indicating that both roots and aggregates play a significant role in SOC accumulation in RMS.
机译:开垦的土壤可以恢复土壤质量和生态系统生产力以及固碳,但关于填海后土地利用和管理对再生矿山土壤(RMS)中土壤有机碳(SOC)储存的影响的数据有限。进行了一项研究,评估了在四个不同的管理实践下(草地,干草,放牧,和放牧喂养。附近未受干扰的草地用作基准或参考。干草和草甸的RMS堆积密度(范围:1.16-1.88 mg m-3)显着低于放牧地点(P <0.05)。此外,在干草和草地实践下,RMS比放牧地点的水稳性骨料(WSA)浓度更高,骨料的平均重量直径(MWD)更大。 RMS中的土壤pH和电导率(EC)高于未扰动的土壤。在开垦的地点中,草甸的pH和EC值通常低于放牧和饲喂饲喂的做法(P <0.05)。放牧和牧草场的SOC(分别为89和76 mg ha-1)通常高于草甸(64 mg ha-1),放牧(70 mg ha-1)和未受干扰的草地(72 mg ha) -1)。数据表明,去除干草上的地上生物量对这些草地的SOC积累没有影响。在开垦的草地中,近50%的根生物量积累在顶部0-10厘米处。 SOC含量与MWD(R2 = 0.70,P <0.01)和根生物量(R2 = 0.75 P <0.01)密切相关,表明根和团粒均在RMS SOC积累中起重要作用。

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