Czech Geological Survey, Klárov 3, 118 21 Prague, Czech Republic; Global Change Research Institute, AS CR, Bělidla 986/4a, 60300 Brno, Czech Republic.
Department of Ecosystem Biology, Faculty of Science, University of South Bohemia, Branišovská 31, 37005 České Budějovice, Czech Republic.
Environ Pollut. 2018 Jul;238:884-893. doi: 10.1016/j.envpol.2018.03.081. Epub 2018 Apr 6.
Increased reactive nitrogen (N) loadings to terrestrial ecosystems are believed to have positive effects on ecosystem carbon (C) sequestration. Global "hot spots" of N deposition are often associated with currently or formerly high deposition of sulphur (S); C fluxes in these regions might therefore not be responding solely to N loading, and could be undergoing transient change as S inputs change. In a four-year, two-forest stand (mature Norway spruce and European beech) replicated field experiment involving acidity manipulation (sulphuric acid addition), N addition (NHNO) and combined treatments, we tested the extent to which altered soil solution acidity or/and soil N availability affected the concentration of soil dissolved organic carbon (DOC), soil respiration (Rs), microbial community characteristics (respiration, biomass, fungi and bacteria abundances) and enzyme activity. We demonstrated a large and consistent suppression of soil water DOC concentration driven by chemical changes associated with increased hydrogen ion concentrations under acid treatments, independent of forest type. Soil respiration was suppressed by sulphuric acid addition in the spruce forest, accompanied by reduced microbial biomass, increased fungal:bacterial ratios and increased C to N enzyme ratios. We did not observe equivalent effects of sulphuric acid treatments on Rs in the beech forest, where microbial activity appeared to be more tightly linked to N acquisition. The only changes in C cycling following N addition were increased C to N enzyme ratios, with no impact on C fluxes (either Rs or DOC). We conclude that C accumulation previously attributed solely to N deposition could be partly attributable to their simultaneous acidification.
人们认为,增加向陆地生态系统输入的活性氮(N)会对生态系统碳(C)固存产生积极影响。全球 N 沉积的“热点”通常与目前或以前高硫(S)沉积有关;因此,这些地区的 C 通量可能不仅仅对 N 加载做出响应,而且随着 S 输入的变化,它们可能正在经历暂态变化。在一项为期四年、涉及两种林分(成熟挪威云杉和欧洲山毛榉)的复制现场实验中,我们进行了酸度操纵(添加硫酸)、N 添加(NHNO)和联合处理,以测试土壤溶液酸度或/和土壤 N 有效性的改变在多大程度上影响土壤溶解有机碳(DOC)浓度、土壤呼吸(Rs)、微生物群落特征(呼吸、生物量、真菌和细菌丰度)和酶活性。我们证明了由于氢离子浓度增加而导致的与酸化相关的化学变化驱动的土壤水 DOC 浓度的大量且一致的抑制,这种抑制与林型无关。硫酸处理抑制了云杉林中的土壤呼吸,同时伴随着微生物生物量减少、真菌:细菌比例增加和 C 到 N 酶比例增加。我们没有观察到硫酸处理对山毛榉林中 Rs 的等效影响,因为微生物活性似乎与 N 吸收更紧密地相关。N 添加后 C 循环的唯一变化是 C 到 N 酶比例增加,对 C 通量(无论是 Rs 还是 DOC)没有影响。我们得出结论,以前归因于 N 沉积的 C 积累可能部分归因于它们的同时酸化。