2017
DOI: 10.1101/164046
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Environmental DNA metabarcoding of rivers: Not all eDNA is everywhere, and not all the time

Abstract: Environmental DNA metabarcoding has become a popular tool for the assessment of freshwater biodiversity, but it is largely unclear how sampling time and location influence the assessment of communities. Abiotic factors in rivers can change on small spatial and temporal scale and might greatly influence eDNA metabarcoding results. In this study, we sampled three German rivers at four locations per sampling site: 1. Left river side, surface water 2. Right river side, surface water, 3. Left side, close to the riv… Show more

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Cited by 28 publications
(35 citation statements)
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References 59 publications
(65 reference statements)
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“…Surprisingly, the 7th stream order sites diverge from this pattern, potentially because we could only access part of these wide river cross sections, and sampling was restricted to the river edge where less mixing occurs, where more extensive sampling may be needed with eDNA (Bylemans et al, ). Also, recent studies indicate that eDNA is not evenly distributed in the water column (Macher & Leese, ), and it is still unclear how spatial variance in structures, such as riffles and ponds, is affecting the mixing of the water column and thus the equal detection of eDNA along the water column. We speculate that only in smaller streams (1st to 5th order), one or two samples from the edge or in the center adequately reflect the eDNA distribution across the river transect, while in larger rivers, multiple samples across the cross section may be recommended.…”
Section: Discussionmentioning
confidence: 99%
“…Surprisingly, the 7th stream order sites diverge from this pattern, potentially because we could only access part of these wide river cross sections, and sampling was restricted to the river edge where less mixing occurs, where more extensive sampling may be needed with eDNA (Bylemans et al, ). Also, recent studies indicate that eDNA is not evenly distributed in the water column (Macher & Leese, ), and it is still unclear how spatial variance in structures, such as riffles and ponds, is affecting the mixing of the water column and thus the equal detection of eDNA along the water column. We speculate that only in smaller streams (1st to 5th order), one or two samples from the edge or in the center adequately reflect the eDNA distribution across the river transect, while in larger rivers, multiple samples across the cross section may be recommended.…”
Section: Discussionmentioning
confidence: 99%
“…Another non‐harmful method that could be used with underwater cameras, and is becoming increasingly popular for detecting rare aquatic species, is environmental DNA (eDNA; Balasingham, Walter, Mandrak, & Heath, ; Boothroyd, Mandrak, Fox, & Wilson, ; Janosik & Johnson, ). This emerging method detects species based on collected genetic material from water samples (Janosik & Johnson, ), but also has some limitations, such as the heterogeneous distribution of eDNA across temporal and spatial scales in a river, reducing the detection of species even at small spatial scales (Macher & Leese, ). This method could be combined with underwater cameras to obtain higher detection probabilities of rare fishes without adverse effects on the species and habitats.…”
Section: Discussionmentioning
confidence: 99%
“…In part, this is due to the fact that the samples and lakes included in this analysis are limited in number and are geographically close to each other [22, 24, 25, 36]. Therefore, for a more thorough analysis, larger datasets from more variable sites would be neccessary, as currently only available from large-scale environmental sequencing efforts such as the Earth Microbiome Project [37] or the 1000 Springs Project [28, 38].…”
Section: Discussionmentioning
confidence: 99%