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. 2019 Nov 18;98(2):354–366. doi: 10.1111/jfb.14176

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© 2019 The Authors. Journal of Fish Biology published by John Wiley & Sons Ltd on behalf of The Fisheries Society of the British Isles.

This is an open access article under the terms of the http://creativecommons.org/licenses/by/4.0/ License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.

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Sampling locations along river stretches (RS) A to E () of the main channel of the Rhône River, France, using both traditional electro‐fishing (TEF) and eDNA. , Sites sampled every 2 months (September 2015– August 2016); , sites where ten eDNA water samples (filtration capsules) were collected once; , sites located on the tributaries or the Rhône River itself sampled once for eDNA. The 10 metric fish index and the adapted six‐metric fish index were computed at all sites with a black filled symbol within natural water bodies

Inline graphic — Sampling locations along river stretches (RS) A to E () of the main channel of the Rhône River, France, using both traditional electro‐fishing (TEF) and eDNA. , Sites sampled every 2 months (September 2015– August 2016); , sites where ten eDNA water samples (filtration capsules) were collected once; , sites located on the tributaries or the Rhône River itself sampled once for eDNA. The 10 metric fish index and the adapted six‐metric fish index were computed at all sites with a black filled symbol within natural water bodies