Department of Physiological Diversity, Helmholtz Center for Environmental Research (UFZ), 04318, Leipzig, Germany.
German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, 04103, Leipzig, Germany.
Oecologia. 2021 Nov;197(3):675-684. doi: 10.1007/s00442-021-05064-w. Epub 2021 Oct 29.
Plant communities worldwide show varied responses to nutrient enrichment-including shifts in species identity, decreased diversity, and changes in functional trait composition-but the factors determining community recovery after the cessation of nutrient addition remain uncertain. We manipulated nutrient levels in a tundra community for 6 years of nutrient addition followed by 8 years of recovery. We examined how community recovery was mediated by traits related to plant resource-use strategy and plant ability to modify their environment. Overall, we observed persistent effects of fertilization on plant communities. We found that plants with fast-growing traits, including higher specific leaf area, taller stature and lower foliar C:N, were more likely to show a persistent increase in fertilized plots than control plots, maintaining significantly higher cover in fertilized plots 8 years after cessation of fertilization. Additionally, although graminoids responded most strongly to the initial fertilization treatment, forb species were more vulnerable to fertilization effects in the long-term, showing persistent decline and no recovery in 8 years. Finally, these persistent fertilization effects were accompanied by modified environmental conditions, including persistent increases in litter depth and soil phosphorous and lower soil C:N. Our results demonstrate the potential for lasting effects of nutrient enrichment in nutrient-limited systems and identify species traits related to rapid growth and nutrient-use efficiency as the main predictors of the persistence of nutrient enrichment effects. These findings highlight the usefulness of trait-based approach for understanding the persistent feedbacks of nutrient enrichment, plant dynamics, and niche construction via litter and nutrient build-up.
全球范围内的植物群落对养分富集表现出不同的响应,包括物种身份的转变、多样性的降低以及功能特征组成的变化,但对于养分添加停止后群落恢复的决定因素仍不确定。我们在一个多年冻土区群落中进行了 6 年的养分添加实验,随后进行了 8 年的恢复实验。我们研究了与植物资源利用策略和植物改变环境能力相关的特征是如何介导群落恢复的。总的来说,我们观察到施肥对植物群落的持续影响。我们发现,具有快速生长特征的植物,包括更高的比叶面积、更高的株高和更低的叶片 C:N,比对照样地更有可能在施肥样地中持续增加,即使在停止施肥 8 年后,它们在施肥样地中的盖度仍保持显著较高。此外,尽管禾本科植物对初始施肥处理反应最强烈,但草本植物在长期内更容易受到施肥的影响,在 8 年内持续下降且没有恢复。最后,这些持续的施肥效应伴随着环境条件的改变,包括凋落物深度、土壤磷和土壤 C:N 的持续增加。我们的研究结果表明,在养分有限的系统中,养分富集的持久效应是可能的,并确定了与快速生长和养分利用效率相关的物种特征,作为养分富集效应持续存在的主要预测因子。这些发现强调了基于特征的方法在理解养分富集、植物动态和通过凋落物和养分积累进行生态位构建的持久反馈方面的有用性。