State Key Laboratory of Vegetation and Environmental Change, Institute of Botany, Chinese Academy of Sciences, Beijing, China.
University of Chinese Academy of Sciences, Beijing, China.
Glob Chang Biol. 2020 Feb;26(2):960-970. doi: 10.1111/gcb.14841. Epub 2019 Oct 1.
Livestock grazing often alters aboveground and belowground communities of grasslands and their mediated carbon (C) and nitrogen (N) cycling processes at the local scale. Yet, few have examined whether grazing-induced changes in soil food webs and their ecosystem functions can be extrapolated to a regional scale. We investigated how large herbivore grazing affects soil micro-food webs (microbes and nematodes) and ecosystem functions (soil C and N mineralization), using paired grazed and ungrazed plots at 10 locations across the Mongolian Plateau. Our results showed that grazing not only affected plant variables (e.g., biomass and C and N concentrations), but also altered soil substrates (e.g., C and N contents) and soil environment (e.g., soil pH and bulk density). Grazing had strong bottom-up effects on soil micro-food webs, leading to more pronounced decreases at higher trophic levels (nematodes) than at lower trophic levels (microbes). Structural equation modeling showed that changes in plant biomass and soil environment dominated grazing effects on microbes, while nematodes were mainly influenced by changes in plant biomass and soil C and N contents; the grazing effects, however, differed greatly among functional groups in the soil micro-food webs. Grazing reduced soil C and N mineralization rates via changes in plant biomass, soil C and N contents, and soil environment across grasslands on the Mongolian Plateau. Spearman's rank correlation analysis also showed that grazing reduced the correlations between functional groups in soil micro-food webs and then weakened the correlation between soil micro-food webs and soil C and N mineralization. These results suggest that changes in soil micro-food webs resulting from livestock grazing are poor predictors of soil C and N processes at regional scale, and that the relationships between soil food webs and ecosystem functions depend on spatial scales and land-use changes.
牲畜放牧通常会改变草地的地上和地下群落及其介导的碳 (C) 和氮 (N) 循环过程,在局部尺度上。然而,很少有人研究放牧引起的土壤食物网及其生态系统功能的变化是否可以外推到区域尺度。我们通过在蒙古高原 10 个地点的放牧和未放牧样地对大型食草动物放牧如何影响土壤微食物网(微生物和线虫)和生态系统功能(土壤 C 和 N 矿化)进行了研究。我们的结果表明,放牧不仅影响植物变量(例如生物量和 C 和 N 浓度),还改变土壤基质(例如 C 和 N 含量)和土壤环境(例如土壤 pH 值和容重)。放牧对土壤微食物网产生了强烈的自上而下的影响,导致较高营养级别的线虫比较低营养级别的微生物更为明显的减少。结构方程模型表明,植物生物量和土壤环境的变化主导了放牧对微生物的影响,而线虫主要受植物生物量和土壤 C 和 N 含量的变化影响;然而,放牧的影响在土壤微食物网的不同功能组之间存在很大差异。放牧通过改变植物生物量、土壤 C 和 N 含量以及土壤环境,降低了草原土壤 C 和 N 矿化速率。Spearman 秩相关分析还表明,放牧减少了土壤微食物网中功能组之间的相关性,从而削弱了土壤微食物网与土壤 C 和 N 矿化之间的相关性。这些结果表明,由于牲畜放牧导致的土壤微食物网的变化是土壤 C 和 N 过程在区域尺度上的不良预测指标,并且土壤食物网与生态系统功能之间的关系取决于空间尺度和土地利用变化。