Abstract

Many degraded ecosystems are subject to restoration attempts, providing new opportunities to unravel the processes of ecological community assembly. Restoration of previously drained northern peatlands, primarily to promote peat and carbon accumulation, has created hundreds of thousands of new open water pools. We assessed the potential benefits of this wetland restoration for aquatic biodiversity, and how communities reassemble, by comparing pool ecosystems in regions of the UK Pennines on intact (never drained) versus restored (blocked drainage-ditches) peatland. We also evaluated the conceptual idea that comparing reference ecosystems in terms of their compositional similarity to null assemblages (and thus the relative importance of stochastic versus deterministic assembly) can guide evaluations of restoration success better than analyses of community composition or diversity. Community composition data highlighted some differences in the macroinvertebrate composition of restored pools compared to undisturbed peatland pools, which could be used to suggest that alternative end-points to restoration were influenced by stochastic processes. However, widely used diversity metrics indicated no differences between undisturbed and restored pools. Novel evaluations of restoration using null models confirmed the similarity of deterministic assembly processes from the national species pool across all pools. Stochastic elements were important drivers of between-pool differences at the regional-scale but the scale of these effects was also similar across most of the pools studied. The amalgamation of assembly theory into ecosystem restoration monitoring allows us to conclude with more certainty that restoration has been successful from an ecological perspective in these systems. Evaluation of these UK findings compared to those from peatlands across Europe and North America further suggests that restoring peatland pools delivers significant benefits for aquatic fauna by providing extensive new habitat that is largely equivalent to natural pools. More generally, we suggest that assembly theory could provide new benchmarks for planning and evaluating ecological restoration success.

Highlights

  • Degraded, damaged or destroyed ecosystems are the subject of ever increasing attempts to effect restoration of ecological processes, conserve biodiversity and sustain the livelihoods of people who depend upon them (Allison, 2012)

  • Trichoptera were found in low abundance but included Limnephilus coenosus which is common in small permanent peatland pools, as well as Polycentropodidae (Polycentropus sp., Plectrocnemia conspersa and Holocentropus spp.)

  • Small but significant differences in macroinvertebrate community composition were found between pool types (PERMANOVA; R2 = 0.09; P = 0.001), region (R2 = 0.17, P = 0.001) and pool type*region (R2 = 0.09; P = 0.001) despite pool environments showing no significant differences in physicochemistry between pool types, either when combined overall or when nested within sampling dates (Table 1)

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Summary

Introduction

Degraded, damaged or destroyed ecosystems are the subject of ever increasing attempts to effect restoration of ecological processes, conserve biodiversity and sustain the livelihoods of people who depend upon them (Allison, 2012). Only 35–44% of restoration programmes across a wide range of ecosystem types have been reported as having favourable outcomes for biodiversity (Benayas et al, 2009; Jones and Schmitz, 2009) leading to the often repeated conclusion that many ecological restoration attempts have been unsuccessful (Lockwood and Pimm, 1999). Significant drivers of changes in ecosystem structure and functioning include dispersal and colonisation success, biotic interactions and feedbacks which can introduce significant stochasticity to community composition (Ledger et al, 2006; Chase, 2007; Heino et al, 2015) and to restoration outcomes. Incorporating knowledge of reference-community assembly processes in the planning or evaluation of restoration programmes has still not begun (Lockwood and Pimm, 1999; Chase, 2007)

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