Laboratory of Geospatial Technology for the Middle and Lower Yellow River Regions, College of Environment and Planning, Henan University, Jinming Avenue, Kaifeng 475004, China.
Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, 723 Xingke Road, Tianhe District, Guangzhou 510650, China.
Environ Pollut. 2018 Apr;235:293-301. doi: 10.1016/j.envpol.2017.12.083. Epub 2018 Jan 4.
World soils are subjected to a number of anthropogenic global change factors. Although many previous studies contributed to understand how single global change factors affect soil properties, there have been few studies aimed at understanding how two naturally co-occurring global change drivers, nitrogen (N) deposition and increased precipitation, affect critical soil properties. In addition, most atmospheric N deposition and precipitation increase studies have been simulated by directly adding N solution or water to the forest floor, and thus largely neglect some key canopy processes in natural conditions. These previous studies, therefore, may not realistically simulate natural atmospheric N deposition and precipitation increase in forest ecosystems. In a field experiment, we used novel canopy applications to investigate the effects of N deposition, increased precipitation, and their combination on soil chemical properties and the microbial community in a temperate deciduous forest. We found that both soil chemistry and microorganisms were sensitive to these global change factors, especially when they were simultaneously applied. These effects were evident within 2 years of treatment initiation. Canopy N deposition immediately accelerated soil acidification, base cation depletion, and toxic metal accumulation. Although increased precipitation only promoted base cation leaching, this exacerbated the effects of N deposition. Increased precipitation decreased soil fungal biomass, possible due to wetting/re-drying stress or to the depletion of Na. When N deposition and increased precipitation occurred together, soil gram-negative bacteria decreased significantly, and the community structure of soil bacteria was altered. The reduction of gram-negative bacterial biomass was closely linked to the accumulation of the toxic metals Al and Fe. These results suggested that short-term responses in soil cations following N deposition and increased precipitation could change microbial biomass and community structure.
世界土壤受到多种人为全球变化因素的影响。尽管许多先前的研究有助于了解单一全球变化因素如何影响土壤特性,但很少有研究旨在了解氮(N)沉积和降水增加这两个自然共同发生的全球变化驱动因素如何影响关键土壤特性。此外,大多数大气 N 沉积和降水增加的研究都是通过直接向林地表层添加 N 溶液或水来模拟的,因此在很大程度上忽略了自然条件下一些关键的冠层过程。因此,这些先前的研究可能无法真实地模拟森林生态系统中的自然大气 N 沉积和降水增加。在一项野外实验中,我们使用新型冠层应用来研究 N 沉积、降水增加及其组合对温带落叶林土壤化学性质和微生物群落的影响。我们发现,土壤化学性质和微生物都对这些全球变化因素敏感,尤其是当它们同时应用时。这些影响在处理开始后的 2 年内就显现出来了。冠层 N 沉积立即加速了土壤酸化、碱基阳离子耗竭和有毒金属积累。尽管增加的降水仅促进了碱基阳离子的淋失,但这加剧了 N 沉积的影响。增加的降水降低了土壤真菌生物量,这可能是由于润湿/再干燥胁迫或 Na 的耗尽所致。当 N 沉积和增加的降水同时发生时,土壤革兰氏阴性菌显著减少,土壤细菌的群落结构发生改变。革兰氏阴性菌生物量的减少与有毒金属 Al 和 Fe 的积累密切相关。这些结果表明,N 沉积和增加的降水后土壤阳离子的短期响应可能会改变微生物生物量和群落结构。