Determination of the gas diffusion coefficient of a peat grassland soil
Summary 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...
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Published in | European journal of soil science Vol. 64; no. 5; pp. 681 - 687 |
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Main Authors | , , , , , |
Format | Journal Article |
Language | English |
Published |
Oxford, UK
Blackwell Publishing Ltd
01.10.2013
Blackwell |
Subjects | |
Online Access | Get full text |
ISSN | 1351-0754 1365-2389 |
DOI | 10.1111/ejss.12056 |
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Abstract | Summary
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 (ϵ) range of 0 and 0.5 cm3 cm−3. Values of Ds for the peat cores ranged between 3.2 × 10−4 and 4.4 × 10−3 m2 hour−1, for loamy clay cores between 0 and 4.7 × 10−3 m2 hour−1 and for the sandy reference soil they were between 5.4 × 10−4 and 3.4 × 10−3 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 ϵ would be beneficial. |
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AbstractList | 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 (D sub(s)). The availability of specific measurements for peatland soils is currently limited. This study measured D sub(s) for a peat soil with an overlying clay horizon and compared values with those from widely available models. The D sub(s) value of a sandy loam reference soil was measured for comparison. Using the Currie (1960) method, D sub(s) was measured between an air-filled porosity ( epsilon ) range of 0 and 0.5 cm super(3) cm super(-3). Values of D sub(s) for the peat cores ranged between 3.2 x 10 super(-4) and 4.4 x 10 super(-3) m super(2) hour super(-1), for loamy clay cores between 0 and 4.7 x 10 super(-3) m super(2) hour super(-1) and for the sandy reference soil they were between 5.4 x 10 super(-4) and 3.4 x 10 super(-3) m super(2) hour super(-1). The agreement of measured and modelled values of relative diffusivity (D sub(s)/D sub(0), with D sub(0) 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 D sub(s) 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 D sub(s) for a greater range of epsilon would be beneficial. 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 ( D s ). The availability of specific measurements for peatland soils is currently limited. This study measured D s for a peat soil with an overlying clay horizon and compared values with those from widely available models. The D s value of a sandy loam reference soil was measured for comparison. Using the Currie (1960) method, D s was measured between an air‐filled porosity ( ϵ ) range of 0 and 0.5 cm 3 cm −3 . Values of D s for the peat cores ranged between 3.2 × 10 −4 and 4.4 × 10 −3 m 2 hour −1 , for loamy clay cores between 0 and 4.7 × 10 −3 m 2 hour −1 and for the sandy reference soil they were between 5.4 × 10 −4 and 3.4 × 10 −3 m 2 hour −1 . The agreement of measured and modelled values of relative diffusivity ( D s / D 0 , with D 0 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 C ampbell model in the absence of accurately measured D s 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 D s for a greater range of ϵ would be beneficial. 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 (ϵ) range of 0 and 0.5 cm³ cm⁻³. Values of Dₛ for the peat cores ranged between 3.2 × 10⁻⁴ and 4.4 × 10⁻³ m² hour⁻¹, for loamy clay cores between 0 and 4.7 × 10⁻³ m² hour⁻¹ and for the sandy reference soil they were between 5.4 × 10⁻⁴ and 3.4 × 10⁻³ 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 ϵ would be beneficial. Summary 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 (ϵ) range of 0 and 0.5 cm3 cm−3. Values of Ds for the peat cores ranged between 3.2 × 10−4 and 4.4 × 10−3 m2 hour−1, for loamy clay cores between 0 and 4.7 × 10−3 m2 hour−1 and for the sandy reference soil they were between 5.4 × 10−4 and 3.4 × 10−3 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 ϵ would be beneficial. |
Author | Boon, A. Cardenas, L. Chadwick, D. R. Nightingale, P. D. Verhoef, A. Robinson, J. S. |
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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... Peatland habitats are important carbon stocks that also have the potential to be significant sources of greenhouse gases, particularly when subject to changes... |
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SubjectTerms | Agronomy. Soil science and plant productions air Biological and medical sciences carbon sinks clay diffusivity drainage systems Earth sciences Earth, ocean, space Exact sciences and technology fertilizer application Fundamental and applied biological sciences. Psychology grassland soils greenhouse gases habitats peat peat soils peatlands porosity shrinkage Soil science Soils Surficial geology |
Title | Determination of the gas diffusion coefficient of a peat grassland soil |
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