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Insights into the representativeness of biodiversity assessment in large reservoir through eDNA metabarcoding

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could be detected. However, the species distribution is very similar among them. Therefore, increasing the sampling effort by adding replicates in fewer locations could increase the num- ber of taxa. It is not the first time that increasing the number of replicates was suggested for river systems. For instance, Shaw et al. [19] already emphasized the same discussion when evaluating a river area in South Australia, where the authors recommend more replicates to increase the chance of detecting DNA fragments from taxa that are patchily distributed, with low abundance, low biomass or rare occurrence. Conclusions We constructed a large-scale biodiversity inventory to evaluate the diversity of a reservoir’s communities, focusing specifically on metazoans and ichthyofauna. Through the use of vari- ous descriptive and statistical metrics, we assessed the robustness of our biodiversity inventory and determined the optimal experimental design. We found that conducting consistent sam- pling at fewer sites with more replicates was more effective in capturing biodiversity. Metabar- coding proved to be a valuable tool, corroborating previous reports based on traditional monitoring surveys and identifying several previously unreported species. Supporting information S1 Fig. Metrics and spatial information regarding the Três Irmãos (TI) reservoir for hydrodynamic modeling. A) Bathymetry distribution across the reservoir. Darker shades show deeper sites. B) Biquadratic quadrangular finite elements for spatial discretization of the model. (PNG)

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S2 Fig. Hydrodynamic modeling for the entire Três Irmãos (TI) reservoir. Maximum cur- rent speed as measured during the A) rainy and B) dry seasons. (PNG) S3 Fig. Computed water renewal rate for the Três Irmãos (TI) reservoir. The water renewal is shown moving from Nova Avanhandava to Três Irmãos reservoir during A) rainy and B) dry scenarios. (PNG) PLOS ONE eDNA metabarcoding reservoir PLOS ONE | https://doi.org/10.1371/journal.pone.0314210 January 24, 2025 17 / 22

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S4 Fig. Probability of identifying fish by sampling for eDNA at different depths. General- ized Linear Model (GLM) showing the probability (y-axis) of sampling fish taxa in different depths (1 meter, 13 meters and 25 meters from the surface) after three samples (x-axis). Each line represents one depth according to the colors in the legend. (PNG) S5 Fig. Statistics from the Discriminant Analysis of Principal Components (DAPC). A) Sum of contribution of each sampled station for the DAPC clustering assignment. Given the differences in sampling size, the pilot sampling is not included. Station abbreviations as in S1 Table. Each bar corresponds to one station, and the value shows the sum of contribu- tion for the six first Principal Components (see Methods). The stations with the highest val- ues are C01, C11 and C10, respectively. B) Rarefaction curve constructed using only samples from C01, C11 and C10, where the curve reaches the plateau curve around eight samples. (PNG) S1 Table. Sampling locations’ information. Description, geographic coordinates, sampling date, water volume, number of replicates, depth and abbreviations. (XLSX) S2 Table. Pair of primers used to amplify the partial sequences of COI, 12SrRNA, and 16SrRNA genes. Sequences and references are shown for each marker. (XLSX) S3 Table. Summary of reads, Amplicon Sequence Variants (ASVs) and Molecular Opera- tional Taxonomic Units (MOTUs) statistics. Based on eDNA analyses of both pilot and sta- tion sampling, values are shown after and before trimming steps. (XLSX)

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S4 Table. List of Amplicon Sequence Variants (ASVs) amplified using eDNA metabarcod- ing. For both pilot and sampling stations included, the molecular marker, frequency, number of samples, length and taxonomic classification information are displayed for each ASVs. (XLSX) S5 Table. Biodiversity inventory for non-fish taxa in the Três Irmãos (TI) reservoir. The inventory was built using previous literature, eDNA and GBIF information. For each taxon, the source of the record is indicated, as well as the reference, if needed. (XLSX) S6 Table. Biodiversity inventory for ichthyofauna in the Três Irmãos (TI) reservoir. The inventory was built using previous literature, eDNA and Global Biodiversity Information Facility (GBIF) information. For each taxon, the source of the record is indicated, as well as the reference, if needed. (XLSX) Acknowledgments We thank Ange´lica Beccato, from Environment and Land Manager at Tijoa´ Energia, for her support and collaboration in developing this work. Author Contributions Conceptualization: Danielle do Amaral, Mauro Rebelo. PLOS ONE eDNA metabarcoding reservoir PLOS ONE | https://doi.org/10.1371/journal.pone.0314210 January 24, 2025 18 / 22

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Data curation: Thaina´ Cortez, Andre´ Torres. Formal analysis: Thaina´ Cortez, Andre´ Torres, Marcelo Cabral, Gabriel Zielinsky. Funding acquisition: Danielle do Amaral, Mauro Rebelo. Investigation: Thaina´ Cortez, Andre´ Torres, Murilo Guimarães, Henrique Pinheiro, Camila Pereira, Giovanni de Castro, Luana Guerreiro, Juliana Americo, Danielle do Amaral, Mauro Rebelo. Methodology: Thaina´ Cortez, Andre´ Torres, Murilo Guimarães, Henrique Pinheiro, Marcelo Cabral, Gabriel Zielinsky, Juliana Americo, Danielle do Amaral. Project administration: Juliana Americo, Danielle do Amaral, Mauro Rebelo. Resources: Danielle do Amaral, Mauro Rebelo. Supervision: Juliana Americo, Danielle do Amaral, Mauro Rebelo. Validation: Henrique Pinheiro, Camila Pereira, Giovanni de Castro, Luana Guerreiro, Mauro Rebelo. Visualization: Thaina´ Cortez, Murilo Guimarães, Henrique Pinheiro, Camila Pereira, Gio- vanni de Castro, Luana Guerreiro, Danielle do Amaral. Writing – original draft: Thaina´ Cortez. Writing – review & editing: Thaina´ Cortez, Andre´ Torres, Murilo Guimarães, Henrique Pin- heiro, Marcelo Cabral, Gabriel Zielinsky, Camila Pereira, Giovanni de Castro, Luana Guer- reiro, Juliana Americo, Danielle do Amaral, Mauro Rebelo. References 1. Gu W, Swihart RK (2004) Absent or undetected? Effects of non-detection of species occurrence on wildlife—habitat models. Biol Conserv 116:195–203 2. Ma¨chler E, Deiner K, Steinmann P, Altermatt F (2014) Utility of environmental DNA for monitoring rare and indicator macroinvertebrate species. Freshwater Science 33:1174–1183

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