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Research article · 2025 · Full text

International Journal of Biology Sciences

Environmental DNA monitoring for detection of rare and invasive aquatic species in river systems

Yelena EfimovYelena Drozdov

Volume 7(1) · Pages 239–242 · DOI: 10.33545/26649926.2025.v7.i1d.829 ↗

Research areasEnvironmental DNA in Biodiversity StudiesFish Ecology and Management StudiesIdentification and Quantification in Food

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Abstract

Author-written

Detecting rare native and early-stage invasive species in flowing water systems poses a persistent challenge for conservation managers. This research evaluated the performance of environmental DNA metabarcoding and species-specific quantitative PCR for monitoring aquatic vertebrate communities across 24 sampling sites along the Angara River system, Irkutsk Oblast, Russia. Water samples (3 L per site) were collected monthly from April through September 2022, filtered through 0.45-µm cellulose nitrate membranes, and extracted using a modified CTAB protocol. eDNA metabarcoding using 12S mitochondrial primers detected 47 fish species, including three classified as regionally rare (Siberian sturgeon, Baikal omul, lenok). Species-specific qPCR achieved detection probabilities of 0.89-0.97 for target species at distances up to 200 m from confirmed populations. Detection probability declined to 0.28 at 500 m and 0.11 at 1,000 m downstream. Two invasive species rotan and Amur sleeper were detected at four previously unrecorded sites. Occupancy modeling estimated that three replicate samples per site achieved 95% detection confidence for species present at densities above 0.5 individuals per 100 m².

Summary

Source-checked

Plain-language reading of the full paper, prepared with AI and checked against the text. Each point links to the authors' own words.

  1. Why it matters

    • Conservation managers struggle to detect rare native species and invasive species in their early stages within flowing water systems. View evidence ↗

      Why it matters

      Conservation managers struggle to detect rare native species and invasive species in their early stages within flowing water systems.

      In the paper's own words

      “Detecting rare native and early-stage invasive species in flowing water systems poses a persistent challenge for conservation managers.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Environmental DNA (eDNA) provides a non-invasive way to monitor rare species, avoiding the habitat disturbance and false negatives associated with traditional methods like netting or electrofishing. View evidence ↗

      Why it matters

      Environmental DNA (eDNA) provides a non-invasive way to monitor rare species, avoiding the habitat disturbance and false negatives associated with traditional methods like netting or electrofishing.

      In the paper's own words

      “For rare species, eDNA offers a non-invasive alternative to electrofishing, netting, or visual surveys, which may disturb sensitive habitats or produce false negatives when populations are small”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Early detection of invasive species is critical for successful management to stop them from establishing self-sustaining populations. View evidence ↗

      Why it matters

      Early detection of invasive species is critical for successful management to stop them from establishing self-sustaining populations.

      In the paper's own words

      “For invasive species, early detection is the single most important factor in successful management identifying new arrivals before they establish self-sustaining populations”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  2. The question

    • The study aimed to evaluate how well eDNA metabarcoding and species-specific quantitative PCR (qPCR) perform in monitoring aquatic vertebrates across 24 sites in the Angara River system. View evidence ↗

      The question

      The study aimed to evaluate how well eDNA metabarcoding and species-specific quantitative PCR (qPCR) perform in monitoring aquatic vertebrates across 24 sites in the Angara River system.

      In the paper's own words

      “This research evaluated the performance of environmental DNA metabarcoding and species-specific quantitative PCR for monitoring aquatic vertebrate communities across 24 sampling sites along the Angara River system, Irkutsk Oblast, Russia.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  3. What they did

    • At each site, three 1 L replicate water samples were collected at mid-depth and filtered through 0.45-µm membranes within 6 hours. View evidence ↗

      What they did

      At each site, three 1 L replicate water samples were collected at mid-depth and filtered through 0.45-µm membranes within 6 hours.

      In the paper's own words

      “At each site, three replicate water samples of 1 L each were collected using sterile Nalgene bottles at mid-depth from a boat. Water was filtered within 6 hours through 0.45-µm cellulose nitrate membranes”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
    • The study used the MiFish-U primer set targeting the 12S mitochondrial rRNA gene for metabarcoding, with sequencing performed on an Illumina MiSeq. View evidence ↗

      What they did

      The study used the MiFish-U primer set targeting the 12S mitochondrial rRNA gene for metabarcoding, with sequencing performed on an Illumina MiSeq.

      In the paper's own words

      “Metabarcoding used the MiFish-U primer set targeting the 12S mitochondrial rRNA gene. Libraries were sequenced on an Illumina MiSeq with 2×250 bp paired-end reads.”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
    • Specific qPCR assays targeting cytochrome b were developed for five target species: Siberian sturgeon, Baikal omul, lenok, rotan, and Amur sleeper. View evidence ↗

      What they did

      Specific qPCR assays targeting cytochrome b were developed for five target species: Siberian sturgeon, Baikal omul, lenok, rotan, and Amur sleeper.

      In the paper's own words

      “Species-specific qPCR assays targeting cytochrome b were developed for five focal species: Siberian sturgeon (Acipenser baerii), Baikal omul (Coregonus autumnalis), lenok (Brachymystax lenok), rotan (Perccottus glenii), and Amur sleeper (Percottus sp.).”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
  4. What they found

    • eDNA metabarcoding detected 47 fish species, which is 78.3% of the 60 species historically recorded in that river reach. View evidence ↗

      What they found

      eDNA metabarcoding detected 47 fish species, which is 78.3% of the 60 species historically recorded in that river reach.

      In the paper's own words

      “Metabarcoding detected 47 fish species across the 24 sampling sites, representing 78.3% of the 60 species historically recorded from this river reach.”

      Page 2

      Found in: Results

      Read it in the full textOpen PDF at page 2 ↗
    • Among the focal species, qPCR detection probability was highest for the invasive rotan (0.97) and lowest for the rare native Siberian sturgeon (0.89). View evidence ↗

      What they found

      Among the focal species, qPCR detection probability was highest for the invasive rotan (0.97) and lowest for the rare native Siberian sturgeon (0.89).

      In the paper's own words

      “qPCR detection probability was highest for rotan (0.97) and lowest for Siberian sturgeon (0.89)”

      Page 2

      Found in: Results

      Read it in the full textOpen PDF at page 2 ↗
    • The invasive rotan was detected at four new sites, extending its known range 47 km upstream. View evidence ↗

      What they found

      The invasive rotan was detected at four new sites, extending its known range 47 km upstream.

      In the paper's own words

      “Rotan was detected at four sites not previously recorded in fisheries surveys, extending its known range 47 km upstream of prior records.”

      Page 2

      Found in: Results

      Read it in the full textOpen PDF at page 2 ↗
    • Detection probability decreases with distance from the source: the mean probability is 0.97 at the source, drops to 0.63 at 200 m, and falls to 0.20 at 1,000 m downstream. View evidence ↗

      What they found

      Detection probability decreases with distance from the source: the mean probability is 0.97 at the source, drops to 0.63 at 200 m, and falls to 0.20 at 1,000 m downstream.

      In the paper's own words

      “Distance (m) | Rare Native | Invasive | Mean | 95% CI | Replicates Needed ... 0 (at source) | 0.94 | 0.99 | 0.97 | 0.93-0.99 | 1 ... 200 | 0.49 | 0.76 | 0.63 | 0.51-0.74 | 3 ... 1,000 | 0.08 | 0.31 | 0.20 | 0.09-0.30 | 8”

      Page 2

      Found in: Introduction

      Read it in the full textOpen PDF at page 2 ↗
    • Occupancy modeling indicated that three replicate samples per site provide 95% detection confidence for species with densities exceeding 0.5 individuals per 100 m². View evidence ↗

      What they found

      Occupancy modeling indicated that three replicate samples per site provide 95% detection confidence for species with densities exceeding 0.5 individuals per 100 m².

      In the paper's own words

      “Occupancy modeling estimated that three replicate samples per site achieved 95% detection confidence for species present at densities above 0.5 individuals per 100 m².”

      Page 1

      Found in: Comprehensive interpretation

      Read it in the full textOpen PDF at page 1 ↗
  5. What it means

    • The authors recommend integrating eDNA methods into the Angara-Baikal biodiversity monitoring framework to complement traditional fisheries surveys. View evidence ↗

      What it means

      The authors recommend integrating eDNA methods into the Angara-Baikal biodiversity monitoring framework to complement traditional fisheries surveys.

      In the paper's own words

      “These findings support the integration of eDNA methods into the Angara-Baikal biodiversity monitoring framework as a complement to traditional fisheries surveys.”

      Page 3

      Found in: Conclusion

      Read it in the full textOpen PDF at page 3 ↗
    • The study was limited by a six-month sampling window that excluded winter, leaving the effect of ice cover on eDNA dynamics unknown. View evidence ↗

      What it means

      The study was limited by a six-month sampling window that excluded winter, leaving the effect of ice cover on eDNA dynamics unknown.

      In the paper's own words

      “The six-month sampling window excluded winter, when ice cover may alter eDNA dynamics.”

      Page 2

      Found in: Limitations

      Read it in the full textOpen PDF at page 2 ↗
    • The 12S metabarcoding marker lacked the resolution to distinguish all congeners, resulting in some species being identified only at the genus level. View evidence ↗

      What it means

      The 12S metabarcoding marker lacked the resolution to distinguish all congeners, resulting in some species being identified only at the genus level.

      In the paper's own words

      “Additionally, taxonomic resolution of the 12S metabarcoding marker cannot distinguish all congeners, and some assignments remained at genus level.”

      Page 2

      Found in: Limitations

      Read it in the full textOpen PDF at page 2 ↗

Visual summary

3 visuals

Illustrations explain the paper; charts are replotted from the paper's own table values.

AI-generated illustration
AI-generated conceptual illustration (invasive fish in a river system). It explains the idea and does not show study data.↗ Enlarge
eDNA Detection Decay
AI-generated conceptual illustration (invasive fish in a river system). It explains the idea and does not show study data.

AI-generated conceptual illustration (invasive fish in a river system). It explains the idea and does not show study data.

Open full-size image ↗

eDNA Detection Decay

AI-generated conceptual illustration (invasive fish in a river system). It explains the idea and does not show study data.

View source evidence ↗
Replotted from source data
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.↗ Enlarge
qPCR Det. Prob.: Siberian sturgeon vs Baikal omul vs Lenok vs Rotan vs Amur sleeper
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Open full-size image ↗

qPCR Det. Prob.: Siberian sturgeon vs Baikal omul vs Lenok vs Rotan vs Amur sleeper

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

View source evidence ↗
Replotted from source data
Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.↗ Enlarge
Rare Native and Invasive and more: 0 (at source) vs 50 vs 100 vs 200 vs 500
Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.

Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.

Open full-size image ↗

Rare Native and Invasive and more: 0 (at source) vs 50 vs 100 vs 200 vs 500

Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.

View source evidence ↗

Figures & tables

From the original paper
eDNA detection results for five focal species across 24 Angara River sampling sitesTable 1Page 2eDNA detection probability as a function of distance downstream from confirmed source populationsTable 2Page 2Detection probability as a function of distance from source population for rare native and invasive aquatic speciesFigure 1Page 2Workflow of the eDNA monitoring pipeline from water sampling through occupancy modeling and species identificationFigure 2Page 3
FULL TEXT Original article · reflowed for reading

Introduction

Can you find a fish without catching it, seeing it, or even being in the same stretch of river? Environmental DNA genetic material shed by organisms into their surroundings through mucus, feces, and cellular sloughing makes this possible [1] . Since the first demonstrations that fish eDNA could be detected in natural water bodies, the field has expanded rapidly into a practical monitoring tool [2,3] . For rare species, eDNA offers a non-invasive alternative to electrofishing, netting, or visual surveys, which may disturb sensitive habitats or produce false negatives when populations are small [4] . For invasive species, early detection is the single most important factor in successful management identifying new arrivals before they establish self-sustaining populations [5] . River systems present specific eDNA challenges. Flowing water transports DNA downstream, meaning a positive detection doesn't necessarily indicate the organism is at the sampling location. Understanding the relationship between detection probability and distance from source is essential for interpreting eDNA results in lotic environments [6,7] . The Angara River, the only outflow of Lake Baikal, supports a fish community of both endemic Baikal species and introduced taxa whose ranges are expanding. This research assessed eDNA monitoring performance for detecting rare native and invasive fish species across the Angara system, conducted from the Baikal Institute of Limnological Biology, Irkutsk [8,9] .

Ethical considerations

All sampling was non-lethal and non-invasive, involving only water collection. No animals were handled or disturbed. Sampling at sites within the Baikal Nature Reserve buffer zone followed additional protocols specified by the reserve administration, including avoidance of spawning areas during April-May. Collected eDNA samples were catalogued and stored in the institute's biobank under biosecurity conditions preventing unauthorized access or release of genetic material.

Methods

Twenty-four sites were established along a 340-km reach of the Angara River from its outlet at Lake Baikal to Bratsk Reservoir. Sites were spaced approximately 15 km apart and included main-channel, side-channel, and tributary confluence locations. At each site, three replicate water samples of 1 L each were collected using sterile Nalgene bottles at mid-depth from a boat. Water was filtered within 6 hours through 0.45-µm cellulose nitrate membranes using a peristaltic pump. Filters were preserved in 95% ethanol at -20 °C. DNA extraction used a modified CTAB protocol optimized for low-biomass environmental samples. Metabarcoding used the MiFish-U primer set targeting the 12S mitochondrial rRNA gene. Libraries were sequenced on an Illumina MiSeq with 2×250 bp paired-end reads.

Species-specific qPCR assays targeting cytochrome b were developed for five focal species: Siberian sturgeon (Acipenser baerii), Baikal omul (Coregonus autumnalis), lenok (Brachymystax lenok), rotan (Perccottus glenii), and Amur sleeper (Percottus sp.). Detection probability was modeled as a function of distance from the nearest confirmed population using multi-scale occupancy models in the unmarked package in R.

Limitations

Several constraints should be acknowledged. River flow velocity varied between 0.3 and 1.8 m/s across sites, affecting eDNA transport distance and dilution rates. Seasonal temperature variation (4-19 °C) influenced eDNA degradation kinetics. The six-month sampling window excluded winter, when ice cover may alter eDNA dynamics. Additionally, taxonomic resolution of the 12S metabarcoding marker cannot distinguish all congeners, and some assignments remained at genus level.

Results

Metabarcoding detected 47 fish species across the 24 sampling sites, representing 78.3% of the 60 species historically recorded from this river reach. Table 1 presents the detection results for the five focal species. Rotan was detected at four sites not previously recorded in fisheries surveys, extending its known range 47 km upstream of prior records. qPCR detection probability was highest for rotan (0.97) and lowest for Siberian sturgeon (0.89), likely reflecting differences in population density and eDNA shedding rates.

Table 1. eDNA detection results for five focal species across 24 Angara River sampling sites
SpeciesStatusSites +Sites -qPCR Det. Prob.Mean CtConfirmed
Siberian sturgeonRare native6180.8934.2±1.8Yes (5/6)
Baikal omulRare native9150.9431.7±2.1Yes (8/9)
LenokRare native4200.9133.8±1.4Yes (4/4)
RotanInvasive7170.9728.4±1.2Yes (7/7)
Amur sleeperInvasive4200.9330.1±1.7Yes (3/4)

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

View original table image
eDNA detection results for five focal species across 24 Angara River sampling sites↗ Enlarge
Table 1
eDNA detection results for five focal species across 24 Angara River sampling sites

eDNA detection results for five focal species across 24 Angara River sampling sites

Open full-size image ↗
Original paper tableSource PDF · page 2 ↗

Table 2 shows the relationship between sampling distance from confirmed populations and detection probability.

Table 2. eDNA detection probability as a function of distance downstream from confirmed source populations
Distance (m)Rare NativeInvasiveMean95% CIReplicates Needed
0 (at source)0.940.990.970.93-0.991
500.870.950.910.85-0.962
1000.710.880.800.72-0.872
2000.490.760.630.51-0.743
5000.210.540.380.24-0.515
1,0000.080.310.200.09-0.308

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

View original table image
eDNA detection probability as a function of distance downstream from confirmed source populations↗ Enlarge
Table 2
eDNA detection probability as a function of distance downstream from confirmed source populations

eDNA detection probability as a function of distance downstream from confirmed source populations

Open full-size image ↗
Original paper tableSource PDF · page 2 ↗

Comprehensive interpretation

The combined results show that eDNA monitoring can reliably detect both rare native and invasive fish species in flowing river systems, with detection probabilities above 0.80 within 100 m of source populations. The steeper decline in detection probability for rare native species reflects their lower population densities and presumably lower eDNA shedding rates. The discovery of rotan at four new sites demonstrates the value of eDNA for early invasive species detection. Three replicate samples per site provided 95% confidence for target species at moderate densities, offering a practical sampling design for routine monitoring programs [6,7] .

Discussion

The detection of 47 fish species by metabarcoding (78.3% of historical records) is consistent with eDNA survey completeness rates of 70-85% reported from other large river systems [10,11] . The species not detected were predominantly rare benthic specialists, whose eDNA shedding rates may be insufficient for capture by mid-water sampling.

The distance-detection decay curves have direct management implications. For rare species monitoring, sampling sites should be within 200 m of suspected habitats to maintain detection probabilities above 0.50. For invasive species surveillance, the broader transport of eDNA (detection at 500 m with probability 0.54) allows more costeffective site spacing when screening large river reaches [12,13] . The extension of rotan's known range by 47 km upstream is concerning because this invasive predator threatens native juvenile salmonids and has expanded rapidly in connected Siberian waterways since the 1990s [14] . Early eDNA detection creates a window for targeted removal before populations become established. The seasonal limitation of this research excluding winter months means year-round eDNA persistence under ice cover remains unknown this system.

Conclusion

This research demonstrated that eDNA monitoring effectively detects both rare native and invasive fish species in the Angara River system. Metabarcoding captured 78.3% of historically recorded species, while targeted qPCR achieved detection probabilities of 0.89-0.97 at source locations. The distance-decay relationship provides practical guidance for optimizing sampling site placement in river monitoring programs.

The detection of invasive rotan at four previously unrecorded sites illustrates the surveillance value of eDNA for early warning of range expansions. These findings support the integration of eDNA methods into the Angara-Baikal biodiversity monitoring framework as a complement to traditional fisheries surveys.

Acknowledgement

Acknowledgements

Figures and tables from the paper

Figure 1. Detection probability as a function of distance from source population for rare native and invasive aquatic species
Detection probability as a function of distance from source population for rare native and invasive aquatic species↗ Enlarge
Figure 1
Detection probability as a function of distance from source population for rare native and invasive aquatic species

Detection probability as a function of distance from source population for rare native and invasive aquatic species

Open full-size image ↗
Original paper figureSource PDF · page 2 ↗
Figure 2. Workflow of the eDNA monitoring pipeline from water sampling through occupancy modeling and species identification
Workflow of the eDNA monitoring pipeline from water sampling through occupancy modeling and species identification↗ Enlarge
Figure 2
Workflow of the eDNA monitoring pipeline from water sampling through occupancy modeling and species identification

Workflow of the eDNA monitoring pipeline from water sampling through occupancy modeling and species identification

Open full-size image ↗
Original paper figureSource PDF · page 3 ↗

References

14 in the original paper
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  14. Reshetnikov AN. The introduced fish Perccottus glenii: a potential threat to European freshwater biodiversity. Journal of Applied Ichthyology. 2003;19(1):16-20.