Högberg Peter, Nordgren Anders, Högberg Mona N, Ottosson-Löfvenius Mikaell, Olsson Per, Linder Sune
Department of Forest Ecology, SLU, Umeå, Sweden.
SEB Exp Biol Ser. 2005:251-67.
Soil-surface CO2 efflux ('soil respiration') accounts for roughly two-thirds of forest ecosystem respiration, and can be divided into heterotrophic and autotrophic components. Conventionally, the latter is defined as respiration by plant roots. In Boreal forests, however, fine roots of trees are invariably covered by ectomycorrhizal fungi, which by definition are heterotrophs, but like the roots, receive sugars derived from photosynthesis. There is also a significant leaching of labile carbon compounds from the ectomycorrhizal roots. It is, therefore, more meaningful in the context of carbon balance studies to include mycorrhizal fungi and other mycorrhizosphere organisms, dependent on the direct flux of labile carbon from photosynthesis, in the autotrophic component. Hence, heterotrophic activity becomes reserved for the decomposition of more complex organic molecules in litter and other forms of soil organic matter. In reality, the complex situation is perhaps best described as a continuum from strict autotrophy to strict heterotrophy. As a result of this, and associated methodological problems, estimates of the contribution of autotrophic respiration to total soil respiration have been highly variable. Based on recent stand-scale tree girdling experiments we have estimated that autotrophic respiration in boreal forest accounts for up to 50-65% of soil respiration during the snow-free part of the year. Girdling experiments and studies of the delta(13)C of the soil CO2 efflux show that there is a lag of a few days between the carbon uptake by photosynthesis and the release by autotrophic soil respiration of the assimilated carbon. In contrast, estimates of 'bomb 14C' and other approaches have suggested that it takes years to decades between carbon uptake via photosynthesis and the bulk of soil heterotrophic activity. Temperature is normally used as a driver in models of soil processes and it is often assumed that autotrophic soil activity is more sensitive to temperature than is heterotrophic activity, but this is questionable. It is inherently difficult to make a precise separation of autotrophic and heterotrophic respiration from soils. The partitioning between these two components is highly variable in space and time, and taxonomic autotrophs and heterotrophs may perform the function of the other group to some degree. Care should be taken to disturb as little as possible the delicate plant-microbe-soil system, and this speaks for non-intrusive isotopic methods. There are, however, problems in modelling the flux of isotopes through this complex system. Girdling of tree stands is a very robust alternative approach to make the distinction between autotrophic and heterotrophic activities, but ultimately kills the trees and cannot, therefore, always be used. A further development would be to block the phloem sugar transport reversibly. We propose that thus assumption needs further critical testing.
土壤表面的二氧化碳通量(“土壤呼吸”)约占森林生态系统呼吸的三分之二,可分为异养和自养成分。传统上,后者被定义为植物根系的呼吸作用。然而,在北方森林中,树木的细根总是被外生菌根真菌覆盖,根据定义,这些真菌是异养生物,但与根系一样,它们也接收来自光合作用的糖分。外生菌根根还会大量淋失不稳定的碳化合物。因此,在碳平衡研究的背景下,将依赖光合作用产生的不稳定碳直接通量的菌根真菌和其他菌根圈生物纳入自养成分中更有意义。因此,异养活动就保留给凋落物和其他形式的土壤有机质中更复杂有机分子的分解。实际上,这种复杂的情况或许最好描述为从严格自养到严格异养的连续体。由于这一点以及相关的方法学问题,自养呼吸对土壤总呼吸贡献的估计值一直变化很大。基于最近的林分尺度树木环割实验,我们估计北方森林中的自养呼吸在一年中无雪期占土壤呼吸的比例高达50 - 65%。树木环割实验以及对土壤二氧化碳通量δ(13)C的研究表明,光合作用吸收碳与自养土壤呼吸释放同化碳之间存在几天的滞后。相比之下,“核弹14C”和其他方法的估计表明,光合作用吸收碳与土壤大部分异养活动之间需要数年到数十年的时间。在土壤过程模型中,温度通常被用作驱动因素,人们常常假定自养土壤活动比异养活动对温度更敏感,但这是值得怀疑 的。要从土壤中精确分离出自养呼吸和异养呼吸本质上是困难的。这两个成分之间的分配在空间和时间上变化很大,而且分类学上的自养生物和异养生物可能在某种程度上发挥另一类生物的功能。应注意尽可能少地干扰脆弱的植物 - 微生物 - 土壤系统,这支持了非侵入性同位素方法。然而,在对同位素通过这个复杂系统的通量进行建模时存在问题。树木林分的环割是区分自养和异养活动的一种非常可靠的替代方法,但最终会杀死树木,因此不能总是使用。进一步的发展将是可逆地阻断韧皮部糖分运输。我们认为这个假设需要进一步严格检验。