一种从理论上考虑浓度传感器动态特性的密闭腔室系统气体流量评估新方法

K. Nomura, Yuki Yamasaki, A. Takada, Y. Sago, D. Yasutake, M. Kitano
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引用次数: 3

摘要

在各种土壤-植物-大气系统的生理生态学研究中,需要精确测定CO2、H2O等温室气体的通量。例如,通过植物冠层的光合作用和呼吸作用对二氧化碳通量进行量化,不仅对了解作物生产力,而且对分析全球碳平衡至关重要。为了估算农田的灌溉需要量和水分利用效率,需要通过蒸散发来量化水通量。农业用地的CH4和N2O通量已被广泛研究,以评估它们对全球变暖的影响。为了测量这些气体通量,可以使用几种方法,每种方法都有优点和局限性。微气象技术,如涡旋相关或鲍文比方法,在不干扰测量场微环境的情况下进行连续测量方面具有明显的优势(m ller等,2009)。然而,这些方法不适用于小规模领域的实验,因为这些方法的某些假设,如足够的提取长度或稳定的条件,不满足(standard,1997;Baldocchi, 2003)。相反,室内方法,即在植被或土壤上放置一个透明的室内,根据室内气体的浓度变化估计气体通量,仍然是小规模油田的唯一方法(Steduto等人,2002年)。通常,试验箱法分为两类:(i)封闭试验箱法和(ii)开放试验箱法(Livingston and Hutchinson, 1995)。封闭室方法在系统简单性方面优于开放室方法,已广泛应用于与不同科目和尺度的气体通量测量相关的众多研究中(Wheeler, 1992;Kitano et al., 1997;Scott et al., 1999;Hoffmann等人,2015;Lesmeister and Koschorreck, 2017)。闭室法通过测量闭室期间短时间内室内空气中气体浓度的变化率来估计气体通量。气体浓度的变化率经常被假设为恒定的,线性回归函数(LR)已拟合到测量的气体浓度变化中,以估计气体通量(Reicosky等人,1990;Nykanen et al., 2003;Juszczak et al., 2012)。然而,由于被测对象和室内空气之间的气体浓度差异在封闭过程中逐渐减小,气体浓度变化的非线性性质已经被认识到,并且有几项研究认为,使用LR可能导致气体的低估
本文章由计算机程序翻译,如有差异,请以英文原文为准。
A New Method of Evaluating Gas Fluxes in a Closed Chamber System with Theoretical Consideration for Dynamic Characteristics of a Concentration Sensor
For various physio-ecological investigations of soilplant-atmosphere systems, the accurate determination of the fluxes of gases such as CO2, H2O, and other greenhouse gases is required. The quantification of CO2 fluxes by photosynthesis and respiration of a plant canopy, for example, is crucial not only for understanding crop productivity but also for analyzing a global carbon balance. The quantification of H2O fluxes by evapotranspiration is required to estimate irrigation requirement and water use efficiency in crop fields. The fluxes of CH4 and N2O from agricultural lands have been widely investigated for evaluating their effects on global warming. To measure these gas fluxes, several methods can be used, each with advantages and limitations. Micrometeorological techniques such as the eddy covariance or Bowen ratio methods have a clear advantage in continuous measurements without disturbing the microenvironment of a measuring field (Müller et al., 2009). These methods, however, are not applicable to experiments in small-scale fields where certain assumptions of these methods, such as sufficient fetch length or stable conditions, are not satisfied (Stannard,1997; Baldocchi, 2003). Conversely, chamber methods, where a transparent chamber is placed over vegetation or soil and gas fluxes are estimated from the concentration changes of the gases in the chamber, have remained the sole method in smallscale fields (Steduto et al., 2002). Typically, chamber methods are classified into two categories: (i) closed chamber method and (ii) open chamber method (Livingston and Hutchinson, 1995). The closed chamber method can be advantageous over the open chamber method in terms of system simplicity and has been widely used in numerous studies related to gas flux measurements of different subjects and scales (Wheeler, 1992; Kitano et al., 1997; Scott et al., 1999; Hoffmann et al., 2015; Lesmeister and Koschorreck, 2017). The closed-chamber method estimates gas fluxes by measuring the rate of change in gas concentrations in the chamber air in a short time during chamber closure. The rates of change in gas concentrations are frequently assumed to be constant, and the linear regression function (LR) has been fit to the measured changes of gas concentrations to estimate gas fluxes (Reicosky et al., 1990; Nykanen et al., 2003; Juszczak et al., 2012). However, the nonlinear nature of changes in gas concentration due to diminishing concentration differences of gases between the measured subject and chamber air during chamber closure has been recognized, and there are several studies arguing that the use of LR can lead to underestimation of gas
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