A comparison of linear and exponential regression for estimating diffusive CH4 fluxes by closed-chambers in peatlands

被引:58
作者
Forbrich, Inke [1 ]
Kutzbach, Lars [1 ,2 ]
Hormann, Annabell [3 ]
Wilmking, Martin [1 ]
机构
[1] Univ Greifswald, Inst Bot & Landscape Ecol, D-17489 Greifswald, Germany
[2] Univ Hamburg, Inst Soil Sci, D-20146 Hamburg, Germany
[3] Univ Potsdam, Inst Geoecol, D-14476 Potsdam, Germany
关键词
Methane; Peatlands; Closed-chamber measurements; Flux calculation; Gas diffusion; Regression; Non-linearity; GAS-EXCHANGE; NUMERICAL EVALUATION; SOIL RESPIRATION; METHANE; EMISSION; N2O; CO2; DYNAMICS; ERROR;
D O I
10.1016/j.soilbio.2009.12.004
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
The closed-chamber method is the most common approach to determine CH4 fluxes in peatlands. The concentration change in the chamber is monitored over time, and the flux is usually calculated by the slope of a linear regression function. Theoretically, the gas exchange cannot be constant over time but has to decrease, when the concentration gradient between chamber headspace and soil air decreases. In this study, we test whether we can detect this non-linearity in the concentration change during the chamber closure with six air samples. We expect generally a low concentration gradient on dry sites (hummocks) and thus the occurrence of exponential concentration changes in the chamber due to a quick equilibrium of gas concentrations between peat and chamber headspace. On wet (flarks) and sedge-covered sites (lawns), we expect a high gradient and near-linear concentration changes in the chamber. To evaluate these model assumptions, we calculate both linear and exponential regressions for a test data set (n = 597) from a Finnish mire. We use the Akaike Information Criterion with small sample second order bias correction to select the best-fitted model. 13.6%, 19.2% and 9.8% of measurements on hummocks, lawns and flarks, respectively, were best fitted with an exponential regression model. A flux estimation derived from the slope of the exponential function at the beginning of the chamber closure can be significantly higher than using the slope of the linear regression function. Non-linear concentration-overtime curves occurred mostly during periods of changing water table. This could be due to either natural processes or chamber artefacts, e.g. initial pressure fluctuations during chamber deployment. To be able to exclude either natural processes or artefacts as cause of non-linearity, further information, e.g. CH4 concentration profile measurements in the peat, would be needed. If this is not available, the range of uncertainty can be substantial. We suggest to use the range between the slopes of the exponential regression at the beginning and at the end of the closure time as an estimate of the overall uncertainty. (C) 2009 Elsevier Ltd. All rights reserved.
引用
收藏
页码:507 / 515
页数:9
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