Abstract:Despite the large number of river restoration projects carried out worldwide, evidence for strong and long-term positive ecological effects of hydromorphological restoration on macroinvertebrates is scarce. To improve the understanding of the success and failure of restoration measures, a standardized field study was carried out in nineteen paired restored and degraded river sections in mid-sized lowland and mountain rivers throughout Europe. We investigated if there were effects of restoration on macroinverte… Show more
“…even small patches may already have a positive effect (see . Moreover, macroinvertebrate richness depended on microhabitat diversity (see Verdonschot et al, 2015). Since restoration projects had no significant effect on microhabitat diversity (see Poppe et al, 2015), this may at least partly explain the missing effect of restoration on macroinvertebrate richness and diversity (see Verdonschot et al, 2015).…”
Section: Selected Results and Recommendationsmentioning
confidence: 99%
“…Moreover, macroinvertebrate richness depended on microhabitat diversity (see Verdonschot et al, 2015). Since restoration projects had no significant effect on microhabitat diversity (see Poppe et al, 2015), this may at least partly explain the missing effect of restoration on macroinvertebrate richness and diversity (see Verdonschot et al, 2015). These results indicate that although projects restoring river planform by widening or remeandering might increase macro-and mesoscale habitat conditions and hence are visually appealing, they often fail at increasing microhabitat diversity relevant for organism groups like macroinvertebrates.…”
Section: Selected Results and Recommendationsmentioning
This introductory paper presents 20 river restoration cases throughout Europe that were investigated in the EU-funded research project REFORM. In the following, this special issue provides seven specific papers that highlight and discuss the effects of restoration on the investigated river-floodplain systems. Additionally, restoration success was estimated from a socio-economic perspective. The first part of this paper presents the overall study concept and the general sampling design of the field investigations. Each study site was examined with the same array of methods, covering habitat composition in the river and its floodplain, three aquatic and two floodplain-related organism groups, as well as food web composition and ''aquatic terrestrial'' interactions as reflected by stable isotopes. An overview of the rivers and the study sites summarizes main attributes of all investigated sites, with emphasis on the large-scale restoration projects. Some of the projects represent the ''state of the art'' restoration approaches for two major European river types: gravel-bed mountain rivers and sand-bed lowland rivers. Concluding, restoration efforts had positive effects even in the small restoration projects investigated but did not increase with project size. No ''single best'' measure could be identified, but river widening generally had a larger effect compared to other restoration measures.
“…even small patches may already have a positive effect (see . Moreover, macroinvertebrate richness depended on microhabitat diversity (see Verdonschot et al, 2015). Since restoration projects had no significant effect on microhabitat diversity (see Poppe et al, 2015), this may at least partly explain the missing effect of restoration on macroinvertebrate richness and diversity (see Verdonschot et al, 2015).…”
Section: Selected Results and Recommendationsmentioning
confidence: 99%
“…Moreover, macroinvertebrate richness depended on microhabitat diversity (see Verdonschot et al, 2015). Since restoration projects had no significant effect on microhabitat diversity (see Poppe et al, 2015), this may at least partly explain the missing effect of restoration on macroinvertebrate richness and diversity (see Verdonschot et al, 2015). These results indicate that although projects restoring river planform by widening or remeandering might increase macro-and mesoscale habitat conditions and hence are visually appealing, they often fail at increasing microhabitat diversity relevant for organism groups like macroinvertebrates.…”
Section: Selected Results and Recommendationsmentioning
This introductory paper presents 20 river restoration cases throughout Europe that were investigated in the EU-funded research project REFORM. In the following, this special issue provides seven specific papers that highlight and discuss the effects of restoration on the investigated river-floodplain systems. Additionally, restoration success was estimated from a socio-economic perspective. The first part of this paper presents the overall study concept and the general sampling design of the field investigations. Each study site was examined with the same array of methods, covering habitat composition in the river and its floodplain, three aquatic and two floodplain-related organism groups, as well as food web composition and ''aquatic terrestrial'' interactions as reflected by stable isotopes. An overview of the rivers and the study sites summarizes main attributes of all investigated sites, with emphasis on the large-scale restoration projects. Some of the projects represent the ''state of the art'' restoration approaches for two major European river types: gravel-bed mountain rivers and sand-bed lowland rivers. Concluding, restoration efforts had positive effects even in the small restoration projects investigated but did not increase with project size. No ''single best'' measure could be identified, but river widening generally had a larger effect compared to other restoration measures.
“…Indeed, higher physical complexity has been related to higher biodiversity in near-natural systems, and losses of biodiversity have been documented for degraded systems with reduced physical complexity (Beisel et al 2000, Passy andBlanchet 2007). Similarly, follow-up studies of habitat restorations in streams and rivers have found that although physical complexity is frequently enhanced, this has often failed to generate the desired responses within target organism groups or ecosystem functions (Pretty et al 2003, Lepori et al 2005, Nilsson et al 2017, though examples of more successful outcomes exist (Miller et al 2010, Verdonschot et al 2016, Frainer et al 2017. Similarly, follow-up studies of habitat restorations in streams and rivers have found that although physical complexity is frequently enhanced, this has often failed to generate the desired responses within target organism groups or ecosystem functions (Pretty et al 2003, Lepori et al 2005, Nilsson et al 2017, though examples of more successful outcomes exist (Miller et al 2010, Verdonschot et al 2016, Frainer et al 2017.…”
Although ecological restoration generally succeeds in increasing physical heterogeneity, many projects fail to enhance biota. Researchers have suggested several possible explanations, including insufficient restoration intensity, or time-lags in ecological responses that prevent detection of significant changes in short-term monitoring programs. This study aims to evaluate whether benthic macroinvertebrate communities responded to an expanded set of stream restoration measures within a study period of one to five years after completion of the restoration project. We studied 10 forest streams in northern Sweden that were channelized in the past for timber floating. Managers subjected six of these streams to habitat restoration, on each of these we selected two reaches, located in close proximity but differing in restoration intensity. In "basic" restored reaches, the restoration managers broke up the channelized banks and returned cobbles and small boulders to the main channel. In "enhanced" restoration reaches, they added additional large wood and boulders to reaches previously subjected to basic restoration, and rehabilitated gravel beds. The remaining four streams were not restored, and thus represent the baseline impacted (channelized) condition. We surveyed stream benthic assemblages before the enhanced restoration (year 2010) and three times afterward between 2011 and 2015. Five years after restoration, macroinvertebrate assemblages at the enhanced restored reaches were more differentiated from channelized conditions than those at basic-restored reaches. This reflected increased relative abundances of the insect orders Ephemeroptera and Trichoptera and the bivalve molluscs Sphaeriidae and decreased relative abundances of Chironomidae (Diptera). Analysis of functional traits provided further insights on the mechanistic explanations driving the recovery, e.g., indicating that the augmented channel retention capacity at enhanced restored reaches favored taxa adapted to slow flow conditions and more effectively retained passive aquatic dispersers. The increased restoration intensity in enhanced restored reaches has resulted in shifts in the composition of benthic macroinvertebrate assemblages, including increases in more sensitive taxa. These shifts became fully apparent five years after the enhanced restoration. Our results emphasize the value of longer-term monitoring to assess ecological responses following restoration, and of undertaking additional restoration as a valuable management option for previously restored sites that failed to achieve biotic recovery.
“…The distribution of invertebrates in lotic ecosystems is typically patchy, often reflecting spatial patterns which are structured around physical, chemical and trophic processes (Silva et al, 2014;Gibbins et al, 2016;Verdonschot et al, 2016). Research examining lotic environments has typically focussed on longitudinal and lateral gradients (environmental and ecological) as exemplified through the river continuum (Vannote et al, 1980;Rosi-Marshall et al, 2016) and flood pulse concepts (Junk et al, 1989;TuriÄ et al, 2015).…”
The distribution of lotic fauna is widely acknowledged to be patchy reflecting the interaction between biotic and abiotic factors. In an in situ field study, the distribution of benthic and hyporheic invertebrates in the heads (downwelling) and tails (upwelling) of riffles were examined during stable baseflow conditions. Riffle heads were found to contain a greater proportion of interstitial fine sediment than riffle tails. Significant differences in the composition of benthic communities were associated with the amount of fine sediment. Riffle tail habitats supported a greater abundance and diversity of invertebrates sensitive to fine sediment such as EPT taxa. Shredder feeding taxa were more abundant in riffle heads suggesting greater availability of organic matter. In contrast, no significant differences in the hyporheic community were recorded between riffle heads and tails. We hypothesise that clogging of hyporheic interstices with fine sediments may have resulted in the homogenisation of the invertebrate community by limiting faunal movement into the hyporheic zone at both the riffle heads and tails. The results suggest that vertical hydrological exchange significantly influences the distribution of fine sediment and macroinvertebrate communities at the riffle scale.
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