Abstract
AbstractPlant 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.
Funder
Finnish Cultural Foundation
Academy of Finland
Helmholtz-Zentrum für Umweltforschung GmbH - UFZ
Publisher
Springer Science and Business Media LLC
Subject
Ecology, Evolution, Behavior and Systematics
Reference71 articles.
1. Adler PB, Fajardo A, Kleinhesselink AR, Kraft NJB (2013) Trait-based tests of coexistence mechanisms. Ecol Lett 16:1294–1306. https://doi.org/10.1111/ele.12157
2. Austrheim G, Eriksson O (2003) Recruitment and life-history traits of sparse plant species in subalpine grasslands. Can J Bot 81:171–182. https://doi.org/10.1139/b03-010
3. Bakker JP, Berendse F (1999) Constraints in the restoration of ecological diversity in grassland and heathland communities. Trends Ecol Evol 14:63–68. https://doi.org/10.1016/S0169-5347(98)01544-4
4. Bartoń K (2019) MuMIn: multi-model inference. In: https://CRAN.R-project.org/package=cowplot. https://cran.r-project.org/web/packages/MuMIn/index.html. Accessed 27 Mar 2020
5. Basto S, Thompson K, Phoenix G, Sloan V, Leake J, Rees M (2015) Long-term nitrogen deposition depletes grassland seed banks. Nat Commun 6:1–6. https://doi.org/10.1038/ncomms7185
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