Abstract

Abstract Peat‐forming wetlands, particularly floating fens that form the initial stages of these ecosystems, are declining globally due to excavation, dehydration and eutrophication. Restoration typically involves reestablishment of early‐successional open‐water stages, with oligotrophic conditions that are characteristic for these systems. However, restoration success is notoriously limited. A potential improvement may be to initiate succession by reintroducing of target plant species. Knowledge is therefore needed on (a) which plant functional groups should be re‐introduced to stimulate fen formation; and (b) how to manage nutrient levels during restoration, considering that plant growth may be slow in oligotrophic conditions. We hypothesized that increasing functional diversity of introduced species would stimulate the formation of peat‐forming target communities, their biomass accumulation and expansion onto open water. We also hypothesized that nutrient availability would mediate the relative contribution of specific functional groups to these effects. We investigated this in 36 artificial outdoor ponds by manipulating plant functional diversity (clonal dominants, clonal stress‐tolerators and interstitials) on constructed rafts with fen‐forming communities, and subjected these to a range of nutrient loadings over 2 years. Increasing functional diversity as well as increasing nutrient loadings had stimulating effects on plant biomass accumulation, cover formation and rhizome growth onto open water. Both complementarity (due to niche partitioning or facilitation) and selection effects were mechanisms underlying the diversity effect, with a constant relative importance over the entire range of nutrient availabilities. Different functional groups were important for biomass production at different nutrient availabilities. Rhizome formation by clonal stress‐tolerators contributed disproportionately to open water colonization, identifying this functional group as key across all nutrient levels. Synthesis and applications. Restoration of floating fen communities can be stimulated during the first 2 years by introducing a high functional diversity of plant species. These include fast‐growing clonal species, clonal stress‐tolerators and interstitials, which facilitate each other. Restoration is dependent on the presence of clonal stress‐tolerators such as Calla palustris, Comarum palustre and Menyanthes trifoliata for expansion onto the open water. Furthermore, restoration can start under a wide range of water nutrient levels, including eutrophic conditions.

Highlights

  • Peat-­forming wetlands provide a multitude of services, including carbon storage, water purification, water retention and habitat provisioning for typical and endangered species; and are of great cultural value to humans (Chimner, Cooper, Wurster, & Rochefort, 2017; Lamers et al, 2015; Mitsch, Bernal, & Nahlik, 2013; Verhoeven, 1992)

  • We anticipated that a third functional group, nonclonal helophytes, would be facilitated by the floating fen formation by either of the two other groups. We investigated this by manipulating functional diversity of experimental wetland plant communities for 2 years, after which we measured the accumulation of biomass as a proxy for vegetation carbon storage, and the formation of plant cover and rhizomes as proxies for colonization of open water

  • Our results show that restoration of peat-­forming ecosystems may benefit from increasing plant functional richness and nutrient availability for the developing communities, because this stimulates plant growth and the colonization of open water by floating vegetation in the initial years after species reintroduction

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Summary

| INTRODUCTION

Peat-­forming wetlands provide a multitude of services, including carbon storage, water purification, water retention and habitat provisioning for typical and endangered species; and are of great cultural value to humans (Chimner, Cooper, Wurster, & Rochefort, 2017; Lamers et al, 2015; Mitsch, Bernal, & Nahlik, 2013; Verhoeven, 1992) These ecosystems have severely declined on a global scale due to excavation, dehydration and eutrophication (Dahl, 2011; Zedler & Kercher, 2005). We hypothesized that (a) increasing functional diversity of introduced species would stimulate the formation of peat-­forming target communities, their biomass accumulation and expansion onto open water; and that (b) nutrient availability would affect the underlying mechanisms and mediate the relative contribution of specific functional groups van ZUIDAM et al. We investigated this by manipulating functional diversity of experimental wetland plant communities for 2 years, after which we measured the accumulation of biomass as a proxy for vegetation carbon storage, and the formation of plant cover and rhizomes as proxies for colonization of open water

| MATERIALS AND METHODS
Findings
| DISCUSSION
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