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How accurately can soil organic carbon stocks and stock changes be quantified by soil inventories?

机译:土壤有机碳库存和库存变化的准确程度可以通过土壤库存来量化吗?

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摘要

Precise determination of changes in organic carbon (OC) stocks is prerequisite to understand the role of soils in the global cycling of carbon and to verify changes in stocks due to management. A large dataset was collected to form base to repeated soil inventories at 12 CarboEurope sites under different climate and land-use, and with different soil types. Concentration of OC, bulk density (BD), and fine earth fraction were determined to 60 cm depth at 100 sampling points per site. We investigated (1) time needed to detect changes in soil OC, assuming future re-sampling of 100 cores; (2) the contribution of different sources of uncertainties to OC stocks; (3) the effect of OC stock calculation on mass rather than volume base for change detection; and (4) the potential use of pedotransfer functions (PTF) for estimating BD in repeated inventories. The period of time needed for soil OC stocks to change strongly enough to be detectable depends on the spatial variability of soil properties, the depth increment considered, and the rate of change. Cropland sites, having small spatial variability, had lower minimum detectable differences (MDD) with 100 sampling points (105 +/- 28 gC m(-2) for the upper 10 cm of the soil) than grassland and forest sites (206 +/- 64 and 246 +/- 64 gC m(-2) for 0-10 cm, respectively). Expected general trends in soil OC indicate that changes could be detectable after 2-15 yr with 100 samples if changes occurred in the upper 10 cm of stone-poor soils. Error propagation analyses showed that in undisturbed soils with low stone contents, OC concentrations contributed most to OC stock variability while BD and fine earth fraction were more important in upper soil layers of croplands and in stone rich soils. Though the calculation of OC stocks based on equivalent soil masses slightly decreases the chance to detect changes with time at most sites except for the croplands, it is still recommended to account for changing bulk densities with time. Application of PTF for the estimation of bulk densities caused considerable underestimation of total variances of OC stocks if the error associated with the PTF was not accounted for, which rarely is done in soil inventories. Direct measurement of all relevant parameters approximately every 10 yr is recommended for repeated soil OC inventories.
机译:准确确定有机碳(OC)储量的变化是了解土壤在全球碳循环中的作用并验证由于管理而导致的储量变化的先决条件。收集了一个大型数据集,以作为在不同气候和土地利用,不同土壤类型的12个CarboEurope站点上重复土壤清单的基础。在每个站点100个采样点处,将OC浓度,堆积密度(BD)和细土分数确定为60 cm深度。我们调查(1)假设将来要重新采样100个岩心,则需要检测土壤OC变化的时间; (2)不同不确定性来源对OC的贡献; (3)OC库存计算对质量而不是体积基础的变化检测的影响; (4)pedotransfer函数(PTF)在重复库存中估算BD的潜在用途。土壤有机碳储量发生足够大的变化以使其可检测所需的时间取决于土壤特性的空间变异性,所考虑的深度增量和变化率。具有较小空间变异性的农田站点的最低可检测差异(MDD)在100个采样点(土壤的上方10 cm处为105 +/- 28 gC m(-2))低于草地和森林站点(206 + / -0-10厘米分别为64和246 +/- 64 gC m(-2))。预期的土壤OC总体趋势表明,如果石质贫瘠的土壤的上部10 cm发生变化,则2-15年后100个样品可以检测到变化。误差传播分析表明,在石块含量低的未扰动土壤中,OC浓度是导致OC储量变化的主要因素,而BD和细土分数在农田的上层土壤和富含石头的土壤中更为重要。尽管根据等效土壤质量计算OC存量会稍微减少除农田以外的大多数站点随时间变化的机会,但仍建议考虑体积密度随时间的变化。如果不考虑与PTF相关的误差,则将PTF应用于堆积密度的估计会大大低估OC存量的总方差,而在土壤清单中很少这样做。建议重复大约每10年一次直接测量所有相关参数,以进行土壤OC清单的重复测量。

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