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Calculating the long-term stable nitrogen sink in northern European forests

机译:计算北欧森林的长期稳定氮汇

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Nitrogen accumulation rates in a boreal Scots pine monoculture in central Sweden and three groups of mixed Scots pine/Norway spruce/silver birch forests in northern Sweden are estimated by using measured and calculated litter fall data, calculated limit values for litter decomposition, and the nitrogen concentration at the limit value (N-limit). Humus has been accumulating in these forests for 120-3000 years. The N-limit value is determined by extrapolating a linear relationship between accumulated litter mass loss and the increasing litter N concentration. Values for foliar litter fall and N, it are used to calculate the quantity of an hypothesized stable N fraction remaining after accumulated mass loss has reached an asymptotic plateau (the limit value). This stable remaining amount of nitrogen is compared to measured year and amounts of N in the humus layers of the forests. Measured rates of N accumulation in humus range from 0.147 to 0.255 g N m(-2) year(-1) differ from estimated rates of N accumulation in humus by 1.8-30.4%, the higher value possibly due to a slow succession from N-poor pine to N-rich birch. not accounted for in the model. Relating the nitrogen accumulated in these forests at maturity to a nitrogen budget based on estimated rates of nitrogen input, N, fixation, denitrification and leaching to the mineral soil gives a good agreement of about 0.30-0.35 g N m(-2) years stored in humus and vegetation at forest maturity. In these forests, this low rate of N accumulation and storage can apparently continue for thousands of years until the system is "reset" by forest fire. We conclude that in undisturbed boreal forests, once N is bound in recalcitrant fractions it is stable, and that the humus is thus a long-term nitrogen sink. (C) 2004 Elsevier SAS. All rights reserved.
机译:瑞典中部的寒带苏格兰松树单一栽培和瑞典北部的三类苏格兰松树/挪威云杉/白桦林混交林中的氮累积速率是通过使用测得和计算的凋落物下降数据,计算出的凋落物分解极限值和氮来估算的浓度达到极限值(N极限)。腐殖质在这些森林中积累了120-3000年。通过推算累积的垫料质量损失与增加的垫料N浓度之间的线性关系来确定N极限值。叶凋落物下降和N的值,用于计算累积质量损失达到渐近平稳(极限值)后假设的稳定N分数的剩余量。将这种稳定的剩余氮量与测得的年和森林腐殖质层中的氮含量进行比较。腐殖质中N积累的测量速率范围为0.147至0.255 g N m(-2)年(-1),与腐殖质中N积累的估算速率相差1.8-30.4%,该值较高可能是由于N的缓慢演替-松木到富氮桦木。未在模型中说明。根据估计的氮输入速率,固氮,固氮,反硝化作用和向矿质土壤的淋溶速率,将成熟森林中积累的氮与氮预算联系起来,可以得出约0.30-0.35 g N m(-2)年的良好协议。在腐殖质和森林成熟时的植被中。在这些森林中,这种低水平的氮积累和存储速率显然可以持续数千年,直到该系统被森林大火“重置”为止。我们得出的结论是,在不受干扰的北方森林中,一旦氮被束缚在顽固的级分中,氮就很稳定,因此腐殖质是长期的氮汇。 (C)2004 Elsevier SAS。版权所有。

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