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Determination of the gas diffusion coefficient of a peat grassland soil.

机译:泥炭草地土壤气体扩散系数的测定。

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Peatland habitats are important carbon stocks that also have the potential to be significant sources of greenhouse gases, particularly when subject to changes such as artificial drainage and application of fertilizer. Models aiming to estimate greenhouse gas release from peatlands require an accurate estimate of the diffusion coefficient of gas transport through soil (Ds). The availability of specific measurements for peatland soils is currently limited. This study measured Ds for a peat soil with an overlying clay horizon and compared values with those from widely available models. The Ds value of a sandy loam reference soil was measured for comparison. Using the Currie (1960) method, Ds was measured between an air-filled porosity ( epsilon ) range of 0 and 0.5 cm3 cm-3. Values of Ds for the peat cores ranged between 3.2x10-4 and 4.4x10-3 m2 hour-1, for loamy clay cores between 0 and 4.7x10-3 m2 hour-1 and for the sandy reference soil they were between 5.4x10-4 and 3.4x10-3 m2 hour-1. The agreement of measured and modelled values of relative diffusivity (Ds/D0, with D0 the diffusion coefficient through free air) varied with soil type; however, the Campbell (1985) model provided the best replication of measured values for all soils. This research therefore suggests that the use of the Campbell model in the absence of accurately measured Ds and porosity values for a study soil would be appropriate. Future research into methods to reduce shrinkage of peat during measurement and therefore allow measurement of Ds for a greater range of epsilon would be beneficial.
机译:泥炭地栖息地是重要的碳库,也有可能成为温室气体的重要来源,尤其是在受到人工排水和肥料施用等变化的影响时。旨在估算从泥炭地释放的温室气体的模型需要准确估算气体在土壤中的传播扩散系数(D s )。目前对于泥炭地土壤的特定测量方法的可用性是有限的。这项研究测量了覆盖粘土层的泥炭土的D s ,并将其与可广泛获得的模型中的值进行了比较。测量了砂壤土参考土壤的D s 值以进行比较。使用Currie(1960)方法,在空气填充孔隙率(ε)范围为0和0.5 cm 3 cm -3 之间测量了D s sup>。泥炭芯的D s 值介于3.2x10 -4 和4.4x10 -3 m 2 小时之间 -1 ,对于介于0和4.7x10 -3 m 2 hour -1 之间的肥沃粘土芯,沙质参考土壤,它们在5.4x10 -4 和3.4x10 -3 m 2 小时 -1 之间。相对扩散率的测量值和模型值(D s / D 0 ,与D 0 通过自由空气的扩散系数)的一致性随土壤类型然而,Campbell(1985)模型为所有土壤提供了最佳的测量值复制。因此,这项研究表明,在没有精确测量的D s 和孔隙率值的情况下,使用Campbell模型是合适的。未来在测量过程中减少泥炭收缩的方法的研究将是有益的,因此可以在更大范围内测量D s

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