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The impact of four decades of annual nitrogen addition on dissolved organic matter in a boreal forest soil

机译:每年四十年的氮添加量对北方森林土壤中溶解性有机物的影响

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Addition of mineral nitrogen (N) can alter the concentration and quality of dissolved organic matter (DOM) in forest soils. The aim of this study was to assess the effect of long-term mineral N addition on soil solution concentration of dissolved organic carbon (DOC) and dissolved organic nitrogen (DON) in Str?san experimental forest (Norway spruce) in central Sweden. N was added yearly at two levels of intensity and duration: the N1 treatment represented a lower intensity but a longer duration (43 yr) of N addition than the shorter N2 treatment (24 yr). N additions were terminated in the N2 treatment in 1991. The N treatments began in 1967 when the spruce stands were 9 yr old. Soil solution in the forest floor O, and soil mineral B, horizons were sampled during the growing seasons of 1995 and 2009. Tension and non-tension lysimeters were installed in the O horizon (n = 6), and tension lysimeters were installed in the underlying B horizon (n = 4): soil solution was sampled at two-week intervals. Although tree growth and O horizon carbon (C) and N stock increased in treatments N1 and N2, the concentration of DOC in O horizon leachates was similar in both N treatments and control. This suggests an inhibitory direct effect of N addition on O horizon DOC. Elevated DON and nitrate in O horizon leachates in the ongoing N1 treatment indicated a move towards N saturation. In B horizon leachates, the N1 treatment approximately doubled leachate concentrations of DOC and DON. DON returned to control levels, but DOC remained elevated in B horizon leachates in N2 plots nineteen years after termination of N addition. We propose three possible explanations for the increased DOC in mineral soil: (i) the result of decomposition of a larger amount of root litter, either directly producing DOC or (ii) indirectly via priming of old SOM, and/or (iii) a suppression of extracellular oxidative enzymes.
机译:添加矿质氮(N)可以改变森林土壤中溶解性有机物(DOM)的浓度和质量。这项研究的目的是评估长期添加的氮对瑞典中部Str?san实验林(挪威云杉)中土壤溶液中溶解有机碳(DOC)和溶解有机氮(DON)浓度的影响。每年以强度和持续时间两个水平添加N:与较短的N2处理(24年)相比,N1处理的强度较低,但持续时间较长(43年)。 1991年,N2处理终止了N的添加。N云处理始于1967年,当时云杉林龄达9年。在1995年和2009年的生长季节中,对森林底层O的土壤溶液和土壤矿物B的层进行了采样。在O层(n = 6)中安装了张力和非张力渗漏计,在O层中安装了张力渗漏计。基本的B层(n = 4):每两周对土壤溶液取样一次。尽管在处理N1和N2中树木生长和O层碳(C)和N储量增加,但N层处理和对照中O层渗滤液中DOC的浓度相似。这表明氮的添加直接抑制了O地平线DOC。在正在进行的N1处理中,O层渗滤液中的DON和硝酸盐升高,表明向N饱和迈进了一步。在B层渗滤液中,N1处理使渗滤液中DOC和DON的浓度大约增加了一倍。 DON恢复到控制水平,但在终止添加N后19年,N2地块B层渗滤液中的DOC仍然升高。对于矿物土壤中DOC的增加,我们提出了三种可能的解释:(i)直接产生DOC或(ii)通过灌注旧的SOM间接产生的大量根屑分解的结果,和/或(iii)a抑制细胞外氧化酶。

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