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Changes in soil properties, microbial biomass, and fluxes of C and N in soil following post-agricultural grassland restoration

机译:农业草原恢复后土壤性质,微生物量及碳,氮通量的变化

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Understanding the dynamics of soil C and N pools and fluxes following grassland restoration in formerly cultivated soils is needed to assess the capacity of this land-use change to return soil properties and function to pre-disturbance conditions. We examined changes in physical (bulk density) and chemical (pH, available P and N, and total stocks of C and N) properties, microbial biomass C and N, and transformation rates of C and N in soil (0-10 cm depth) across a 35-year chronosequence of prairie restorations and never-cultivated (native) prairie to evaluate the rate and extent to which sowing native perennial plants into formerly cultivated soils returns soil to steady state conditions. Bulk density, available P, and extractable inorganic N decreased exponentially across the chronosequence. Soil pH increased linearly across the chronosequence to exceed that in native prairie soil. Total C and N stocks in cultivated soil were 50% that of native prairie, and increased at rates of 26.2 g C m(-2) year(-1) and 1.68 g N m(-2) year(-1) across the chronosequence. In the oldest restoration, total C and N stocks were 55% and 41% higher than the cultivated soil, respectively. Recovery of C and N stocks to levels comparable to native prairie soil was estimated to take 350 years. Microbial biomass C and N increased 5-fold. Potential C mineralization rate was comparable to native prairie soil following two decades of restoration, and exceeded native prairie in the 35-years restoration. In situ soil CO2 efflux reached equilibrium in 30 years. Potential net N mineralization rate, however, did not exhibit a directional change across the restoration chronosequence, but was lowest in the oldest restored grasslands. Thus, cessation of tillage and sowing native vegetation leads to rapid decreases in available N and P, and promotes rapid (decadal scale) recovery of labile soil organic matter pools, but recovery of total C and N pools requires several centuries. This study suggests that soil properties related to nutrient retention and regulation of nutrient availability can be reestablished within the first few decades of restoration, while C sequestration will continue on a longer time scale. Published by Elsevier B.V.
机译:需要了解在以前耕种的土​​壤中恢复草地后土壤C,N池和通量的动态,以评估这种土地利用变化使土壤性质和功能恢复到干扰前状态的能力。我们研究了物理(体密度)和化学(pH,有效磷和氮以及碳和氮的总存量)特性,微生物生物量碳和氮以及土壤(0-10厘米深度)中碳和氮的转化率的变化),在经过35年的草原恢复和未耕种(原生)草原的时间序列上,评估将多年生原生植物种植到以前耕种的土​​壤中使土壤恢复到稳定状态的速率和程度。在整个时间序列中,堆密度,有效磷和可萃取无机氮呈指数下降。在整个时间序列中,土壤pH线性增加,超过了天然草原土壤中的pH。耕作土壤中的总碳和氮储量少于天然草原的50%,并且在整个期间以26.2 g C m(-2)年(-1)和1.68 g N m(-2)年(-1)的速率增加时间序列。在最旧的修复体中,总的碳和氮储量分别比耕种土壤高55%和41%。估计将碳和氮的储量恢复到与原始草原土壤相当的水平需要350年。微生物生物量碳和氮增加了5倍。经过20年的恢复,潜在的C矿化速率与原始草原土壤相当,并在35年的恢复过程中超过了原始草原。在不到30年的时间里,土壤中的CO2外排达到了平衡。然而,潜在的净氮矿化率在恢复的时间序列上没有表现出方向性变化,但在最古老的恢复草地中最低。因此,停止耕作和播种原生植被会导致有效氮和磷的迅速减少,并促进不稳定土壤有机质池的快速(年代际规模)恢复,但总碳和氮池的恢复需要几个世纪的时间。这项研究表明,与养分保留和养分利用率调节有关的土壤特性可以在恢复的最初几十年内重新建立,而固碳将在更长的时间内继续进行。由Elsevier B.V.发布

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