Spatial Representativeness of Environmental DNA Metabarcoding Signal for Fish Biodiversity Assessment in a Natural Freshwater System
RESEARCH ARTICLE
Spatial Representativeness of Environmental
DNA Metabarcoding Signal for Fish
Biodiversity Assessment in a Natural
Freshwater System
Raphaël Civade1*, Tony Dejean2, Alice Valentini2, Nicolas Roset3, JeanClaude Raymond3, Aurélie Bonin4,5, Pierre Taberlet4,5, Didier Pont1
a11111
1 Hydrosystems and Bioprocesses Research unit, IRSTEA, Antony, France, 2 SPYGEN, Le Bourget du
Lac, France, 3 Rhône-Alpes Regional Direction, ONEMA, Bron, France, 4 Laboratoire d'Ecologie Alpine
(LECA), CNRS, Grenoble, France, 5 Laboratoire d'Ecologie Alpine (LECA), Université Grenoble-Alpes,
Grenoble, France
*
OPEN ACCESS
Citation: Civade R, Dejean T, Valentini A, Roset N,
Raymond J-C, Bonin A, et al. (2016) Spatial
Representativeness of Environmental DNA
Metabarcoding Signal for Fish Biodiversity
Assessment in a Natural Freshwater System. PLoS
ONE 11(6): e0157366. doi:10.1371/journal.
pone.0157366
Editor: Carlos Garcia de Leaniz, Swansea
University, UNITED KINGDOM
Received: December 21, 2015
Accepted: May 27, 2016
Published: June 30, 2016
Copyright: © 2016 Civade et al. This is an open
access article distributed under the terms of the
Creative Commons Attribution License, which permits
unrestricted use, distribution, and reproduction in any
medium, provided the original author and source are
credited.
Data Availability Statement: Sequences for the
reference are available on Dryad doi: 10.5061/dryad.
jm58p. All Illumina raw sequences data are available
on Dryad doi:10.5061/dryad.kp6n4. Inventories from
traditional sampling sessions are available on http://
www.image.eaufrance.fr/poisson/cours/p-ce-resultats.
htm.
Abstract
In the last few years, the study of environmental DNA (eDNA) has drawn attention for many
reasons, including its advantages for monitoring and conservation purposes. So far, in
aquatic environments, most of eDNA research has focused on the detection of single species using species-specific markers. Recently, species inventories based on the analysis of
a single generalist marker targeting a larger taxonomic group (eDNA metabarcoding) have
proven useful for bony fish and amphibian biodiversity surveys. This approach involves in
situ filtering of large volumes of water followed by amplification and sequencing of a short
discriminative fragment from the 12S rDNA mitochondrial gene. In this study, we went one
step further by investigating the spatial representativeness (i.e. ecological reliability and signal variability in space) of eDNA metabarcoding for large-scale fish biodiversity assessment
in a freshwater system including lentic and lotic environments. We tested the ability of this
approach to characterize large-scale organization of fish communities along a longitudinal
gradient, from a lake to the outflowing river. First, our results confirm that eDNA metabarcoding is more efficient than a single traditional sampling campaign to detect species
presence, especially in rivers. Second, the species list obtained using this approach is comparable to the one obtained when cumulating all traditional sampling sessions since 1995
and 1988 for the lake and the river, respectively. In conclusion, eDNA metabarcoding gives
a faithful description of local fish biodiversity in the study system, more specifically within a
range of a few kilometers along the river in our study conditions, i.e. longer than a traditional
fish sampling site.
Funding: In addition to their participation to field
work, data collection and preparation of the
manuscript, ONEMA (French National Agency for
Water and Aquatic Environments) and SPYGEN
PLOS ONE | DOI:10.1371/journal.pone.0157366 June 30, 2016
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Spatial Fish Assemblages Using eDNA Metabarcoding
financially supported this work (Contract IRSTEASPYGENONEMA, 2012-2015). EDF (Electricity of
France) also supported financially this study. The
funders had no role in study design, data collection
and analysis, decision to publish, or preparation of
the manuscript.
Competing Interests: The authors have read the
journal's policy and the authors of this manuscript
have the following competing interests: PT is coinventor of a patent on "teleo" primers and on the use
of the amplified fragment for identifying fish species
from environmental samples. This patent only
restricts commercial applications and has no impact
on the use of this method by academic researchers.
AV and TD are research scientists in a private
company (SPYGEN), specialized on the use of eDNA
for species detection. The private companies EDF
and SPYGEN participated at this study, but this does
not alter the authors' adherence to PLOS ONE
policies on sharing data and materials.
Introduction
Environmental DNA (eDNA) corresponds to the DNA extracted from an environmental sample such as soil, water or feces without first isolating any target organisms. Total eDNA contains cellular DNA originating from living cells or organisms, and extracellular DNA resulting
from natural cell death and subsequent destruction of cell structure [1]. In the last few years,
eDNA analysis has drawn the attention of many ecologists as it is non-invasive [2,3], cost-effective [4,5], more sensitive than traditional methods [6], and useful for monitoring and conservation purposes [3,6–10]. Environmental DNA can be used either to detect single invasive or
endangered species with species-specific markers, or to describe species diversity for a given
taxonomic group using a generalist molecular marker (eDNA metabarcoding [1]).
In freshwater environments, the eDNA metabarcoding approach is increasingly adopted
both in mesocosm and in situ experiments [5,11–14], and it is particularly interesting for large
scale biomonitoring as recommended by recent European directives (e.g. Water Framework
Directive, 2000 [15]). Recently, Valentini et al. [13] proposed a new eDNA metabarcoding
workflow based on markers targeting fish and amphibians, which were validated in silico and
in vitro. Compared with traditional in situ sampling, eDNA analysis was found to be more efficient to assess species richness. However, in addition to the issues inherent to any DNA study
such as contaminations or PCR errors, eDNA studies suffer from specific limitations that
should be acknowledged and properly assessed [16–18]. This is necessary to ensure reliability
of the results and, ultimately, to interpret the eDNA signal detected in natural aquatic ecosystems [16–18].
In mesocosms, eDNA has been shown to remain detectable from a few days to a few weeks
after its release in water [19–22]. Nonetheless, mesocosm studies remain imperfect, as it
is difficult to model the complexity of natural ecosystems with all the factors potentially
involved [16]. For example, eDNA of target species is usually in higher concentrations in
mesocosms than in natural ecosystems. In the case of river ecosystems, the distance of detection depends not only on eDNA persistence, but also on the water flow and can therefore be
highly variable. For example, (...truncated)