Abstract

Most assessments of the effectiveness of river restoration are done at small spatial scales (<10 km) over short time frames (less than three years), potentially failing to capture large‐scale mechanisms such as completion of life‐history processes, changes to system productivity, or time lags of ecosystem responses. To test the hypothesis that populations of two species of large‐bodied, piscivorous, native fishes would increase in response to large‐scale structural habitat restoration (reintroduction of 4,450 pieces of coarse woody habitat into a 110‐km reach of the Murray River, southeastern Australia), we collected annual catch, effort, length, and tagging data over seven years for Murray cod (Maccullochella peelii) and golden perch (Macquaria ambigua) in a restored “intervention” reach and three neighboring “control” reaches. We supplemented mark–recapture data with telemetry and angler phone‐in data to assess the potentially confounding influences of movement among sampled populations, heterogeneous detection rates, and population vital rates. We applied a Bayesian hierarchical model to estimate changes in population parameters including immigration, emigration, and mortality rates. For Murray cod, we observed a threefold increase in abundance in the population within the intervention reach, while populations declined or fluctuated within the control reaches. Golden perch densities also increased twofold in the intervention reach. Our results indicate that restoring habitat heterogeneity by adding coarse woody habitats can increase the abundance of fish at a population scale in a large, lowland river. Successful restoration of poor‐quality “sink” habitats for target species relies on connectivity with high‐quality “source” habitats. We recommend that the analysis of restoration success across appropriately large spatial and temporal scales can help identify mechanisms and success rates of other restoration strategies such as restoring fish passage or delivering water for environmental outcomes.

Highlights

  • Fish populations are imperiled globally (Dudgeon et al 2006) and under increasing threat from human population growth and climate change (Pauly et al 2002, Ficke et al 2008)

  • The two species in this study are medium- to largebodied native freshwater fish (Murray cod [>50 kg and 1,400 mm maximum size, with females reproductively mature at 500 mm length with up to 100,000 eggs produced in large females; see Appendix S1: Plate S1], and golden perch [>10 kg and 600 mm maximum size, with females reproductively mature at 300 mm length with up to 500,000 eggs produced in large females]) with a strong association with instream habitats that they use for refuge, cover for ambushing prey, and spawning sites (Koehn and Nicol 2014)

  • Multiple size classes were represented in the Murray cod population; there was a clear effect of angling on larger cohorts with a sharp decline in abundance of fish over 500 mm (>500 mm are subjected to angling pressure; Appendix S1: Fig. S2), while golden perch were represented primarily by larger cohorts (>300 mm; Appendix S1: Fig. S3)

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Summary

Introduction

Fish populations are imperiled globally (Dudgeon et al 2006) and under increasing threat from human population growth and climate change (Pauly et al 2002, Ficke et al 2008). Fishery and conservation managers work closely with fishery biologists to implement programs that aim to restore rivers and Manuscript received 29 August 2018; revised 11 December 2018; accepted 3 January 2019.

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