Testing predictions of changes in benthic invertebrate abundance and community structure after flow restoration in a large river (French Rhône). (28th March 2015)

• Record Type: Journal Article
• Authors: Mérigoux, Sylvie; Forcellini, Maxence; Dessaix, Jeanne; Fruget, Jean‐François; Lamouroux, Nicolas; Statzner, Bernhard
• Is Part Of: Freshwater biology. Volume 60:Number 6(2015:Jun.)
• Page Start: 1104
• Page End: 1117
• Publication Date: 2015-03-28
• Subjects: Freshwater biology -- Periodicals; Biologie d'eau douce -- Périodiques; 577.605
• DOI: 10.1111/fwb.12422
• Languages: English
• ISSNs: 0046-5070

Abstract

<abstract abstract-type="main" id="fwb12422-abs-0001"> <title>Summary</title> <p> <list id="fwb12422-list-0001" list-type="order"> <list-item> <p>Principal threats to running waters are linked to human‐made discharge modifications, but tools to predict the quantitative consequences of flow restoration for benthic invertebrates in large rivers remain untested.</p> </list-item> <list-item> <p>Quantitative benthos samples from two bypassed reaches (Pierre‐Bénite – PBE – and Chautagne – CHAU) of the French Rhône River were collected during four years each before and after minimum flow increases (from 10 to 100 m<sup>3</sup> s<sup>−1</sup> at PBE and from 10 to 50 m<sup>3</sup> s<sup>−1</sup> at CHAU). These samples provided observed ln‐density changes for the 50 and 62 (PBE and CHAU, respectively) most abundant taxa (typically species or genera). For about half of the 'model' taxa among them, distinct preference models for bottom shear stress categories were available from four reaches of the Upper Rhône River and from various German rivers. Linking these preference models with a statistical hydraulic model predicting frequencies of shear stress categories for any given discharge, we predicted ln‐density changes of the model taxa after restoration.</p> </list-item> <list-item> <p>Community structure of the abundant taxa changed clearly and rapidly after restoration at PBE but less clearly at CHAU. Our predictions explained a considerable amount of mean ln‐density changes of our model taxa observed after restoration (75 and 30% at PBE and CHAU, respectively). They also explained (67 and 40% at PBE and CHAU, respectively) the model taxa scores along the principal components analysis axis that summarised the community variations of all abundant taxa before and after restoration. For taxa not identified to species (assessed as genus, tribe or family), the predicted ln‐density changes were sometimes inaccurate at PBE (a Lower Rhône site), suggesting that the transferability of preference models for taxonomic levels above that of species can be problematic.</p> </list-item> <list-item> <p>If further developed, statistical habitat models focussing on ecologically relevant physical variables (in our case shear stress) should enable reliable quantitative assessments of associations between flow restoration efforts and achievable ecological improvement.</p> </list-item> </list> </p> </abstract>