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Dynamics of net ecosystem CO2 exchange and heterotrophic soil respiration following clearfelling in a drained peatland forest

机译:枯竭的泥炭地森林净砍伐后净生态系统CO2交换和异养土壤呼吸的动态

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In this study we show for the first time with gas exchange measurements, how ecosystem C dynamics evolve after clearfelling in a peatland forest. Clearfelling decreases peat decomposition rate through two mechanisms: aerated peat volume decreases when water-table rises, and increased surface dryness (increased irradiation) limits decomposition of litter. However, since trees are removed and ground vegetation suffers greatly after clearfelling, photosynthesis is low and the site is losing C after clearfelling. New tree stand is needed to shift this direction. Northern forested peatlands contain a large pool of terrestrial carbon (C). When drained for forestry, these peatlands may become sources of C or remain C sinks, depending on site nutrient level, climate, and average water level depth. However, previous studies do not consider the impact of other silvicultural practices on the C dynamics in drained peatlands. Clearfellings cause disturbance in ecosystem C dynamics and might lead to losses of C to the atmosphere. The initial development of C dynamics following clearfelling in a drained peatland forest in Finland was investigated in a 4-year study which included monitoring of ground vegetation development and chamber based measurements of net ecosystem exchange (NEE), ecosystem respiration (R ECO) and heterotrophic peat soil respiration (R PEAT). NEE measurements showed that the site was mainly a net CO2 source (May-October mean efflux of 1990gCO2 ma degree 2 seasona degree 1) to the atmosphere during the three measurement seasons after clearfelling. This was caused by decrease in photosynthesizing biomass and by high R ECO (May-October mean efflux of 2540gCO2 ma degree 2 seasona degree 1). The recovery of ground vegetation biomass was rather fast. However, during the 3 years after clearfelling its capability to fix carbon could not compensate the high R ECO, which was mainly caused by excessive amounts of easily decomposable fresh organic matter (dying tree roots, logging residue and dying ground vegetation). Clearfelling slightly decreased the decomposition rates of peat (R PEAT) (May-October mean efflux of 1130gCO2 ma degree 2 seasona degree 1) i.e., the oldest and largest C storage of the site, through two mechanisms: R PEAT in deeper layers was restricted by higher water table level and in surface layers by excessive dryness, which lowered the temperature response of R PEAT. We conclude that clearfelling strongly affects ecosystem C dynamics but does not affect the peat C storage. The appearance of new tree stand is needed before the ecosystem could act as a C sink again.
机译:在这项研究中,我们首次通过气体交换测量显示了在泥炭地森林中砍伐后生态系统C的动力学如何演变。 Clearfelling通过两种机制降低了泥炭的分解速率:当地下水位升高时,充气泥炭的体积减少,而表面干燥度的增加(辐照度的增加)则限制了垃圾的分解。但是,由于砍伐后树木被砍伐并且地面植被遭受了很大的破坏,因此光合作用低,并且砍伐后该地点的碳损失降低。需要新的树架来改变这个方向。北部森林的泥炭地含有大量的陆地碳(C)。当排干用于林业时,这些泥炭地可能成为C的来源或仍然是C的汇,这取决于现场的养分水平,气候和平均水位深度。但是,先前的研究没有考虑其他造林实践对排水泥炭地碳动态的影响。清除木料会破坏生态系统碳的动力学,并可能导致碳向大气的损失。在一项为期4年的研究中,研究了芬兰干旱的泥炭地森林砍伐后碳动态的最初发展,该研究包括监测地面植被的发育以及基于室的净生态系统交换(NEE),生态系统呼吸(R ECO)和异养性测量泥炭土壤呼吸(R PEAT)。 NEE的测量结果表明,在清除之后的三个测量季节中,该地点主要是向大气中的净CO2排放源(5月至10月,平均2度1季节的平均外排量)。这是由于光合作用生物量的减少和较高的R ECO(5月至10月平均2度1季节的2540gCO2外排)引起的。地面植被生物量的恢复相当快。但是,在清除树木后的三年中,其固定碳的能力无法补偿高的R ECO,这主要是由于过量的易分解的新鲜有机物(垂死的树根,伐木残渣和垂死的植被)引起的。 Clearfelling通过以下两种机制略微降低了泥炭的分解速率(R PEAT)(5月至10月平均流出量为1130gCO2,ma等级2季节,等级1),即该地点的最老和最大的C储存量:较高的地下水位和过高的干燥度会降低R PEAT的温度响应。我们得出的结论是,清除伐木会强烈影响生态系统碳的动态,但不会影响泥炭的存储。在生态系统再次充当C汇之前,需要出现新的林分。

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