PONDWEEDS MARIA KUZMINA UNIVERSITY OF GUELPH, CANADA PONDWEEDS WITH - - PowerPoint PPT Presentation

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PONDWEEDS MARIA KUZMINA UNIVERSITY OF GUELPH, CANADA PONDWEEDS WITH - - PowerPoint PPT Presentation

PONDWEEDS MARIA KUZMINA UNIVERSITY OF GUELPH, CANADA PONDWEEDS WITH US FORESTS IN THE WATER, UNDER AND ABOVE Linear-leaved Broad-leaved Diversifolius WHY MONITORING THEM AND WHAT MAKES IT DIFFICULT? Ecological studies : food and


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SLIDE 1

PONDWEEDS

MARIA KUZMINA UNIVERSITY OF GUELPH, CANADA

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SLIDE 2
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SLIDE 3

PONDWEEDS WITH US – FORESTS IN THE WATER, UNDER AND ABOVE

Linear-leaved Broad-leaved Diversifolius

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SLIDE 4

WHY MONITORING THEM AND WHAT MAKES IT DIFFICULT?

  • Ecological studies: food and shelter for many

species of organisms

  • Bioindication: species-specialists and

generalists towards the alkalinity and pollution

  • Protection: 6 species at risk or special concern

in North America, among those 2 from Ontario (Hill’s and Ogden’s pondweeds)

  • Aquatic habitats less accessible compared to

terrestrial ones

  • Morphologic identification is limited by phenology

and microscopic characters

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SLIDE 5

WHAT ARE THEY AND HOW MANY?

ALISMATALES POTAMOGETONACEAE

Potamogeton (32-37 species) Stuckenia (4 species) Zannichellia (1 species)

30 species in Ontario

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SLIDE 6

BACKGROUND AND OBJECTIVES

Detection of the species of pondweeds (Potamogetonaceae) in water samples

  • Invasive aquatic species

(Scriver et al., 2015) eDNA detection of plants

BROAD SPECIFIC

  • Large-scale monitoring in soil

(Fahner et al., 2016) Requested and funded by the Species at Risk Research Fund

  • f Ontario

(SARRFO, 2016- 2017,10K)

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SLIDE 7

PREPARING LOCAL REFERENCE LIBRARY

30 species of pondweeds reported from Ontario (VASCAN) 90 specimens: collection of DNA from CBG, part of “The Vascular Plants of Canada” project (dx.doi.org/10.5883/DS-POTAM) Potamogeton foliosus (Agriculture and Agrifood Herbarium, DAO) identified by Barre Hellquist*, the author of the treatment of pondweeds in the “Flora of North America”

* *

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SLIDE 8

g

  • atpB-rbcL (Ito et al., 2014)
  • ITS2 (China Plant BOL Group, 2011)

SELECTION OF THE MARKERS & DESIGNING THE PRIMERS

Datasets downloaded from GenBank (atpB-rbcL) & BOLD (ITS2) Datasets of atpB-rbcL & ITS2 generated for the local library

g

Designing primers specific for Potamogetonaceae Designing eDNA primers

eDNA marker (with mean length) Length (bp)

atpB-rbcL-117

101 ‒ 133

atpB-rbcL-184

161 ‒ 208

ITS2-157

133 ‒ 182

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SLIDE 9

SPECIES RESOLUTION WITH THE SELECTED eDNA MARKERS

Species
  • P. foliosus
  • P. friesii
  • P. subsibiricus
  • P. vaseyi
  • P. hillii
  • P. pusillus
  • P. strictifolius
  • P. zosteriformis
  • P. richardsonii
  • P. perfoliatus
  • P. alpinus
  • P. illinoensis
  • P. amplifolius
  • P. pulcher
  • P. epihydrus
  • P. confervoides
  • P. praelongus
  • P. oakesianus
  • P. natans
  • P. gramineus
  • P. crispus
  • P. robbinsii
  • P. spirillus
  • P. bicupulatus
  • S. filiformis
  • S. vaginata
  • S. pectinata
  • Z. palustris
  • P. foliosus
22 23 23 30 30 30 30 8 8 7 9 2 2 1 1 1 1 1 8 7 8 9 9 13 12 15 20
  • P. friesii
22 1 1 51 51 51 51 28 28 27 29 22 22 21 21 21 21 21 28 27 28 29 29 33 32 35 40
  • P. subsibiricus
23 1 2 52 52 52 52 29 29 28 30 23 23 22 22 22 22 22 29 28 29 30 30 34 33 36 41
  • P. vaseyi
23 1 2 50 50 50 50 29 27 28 30 23 23 22 22 22 22 22 29 28 29 30 30 34 33 36 41
  • P. hillii
30 51 52 50 36 35 36 37 31 31 30 30 30 30 30 37 36 37 37 37 41 40 42 47
  • P. pusillus
30 51 52 50 36 35 36 37 31 31 30 30 30 30 30 37 36 37 37 37 41 40 42 47
  • P. strictifolius
30 51 52 50 36 35 36 37 31 31 30 30 30 30 30 37 36 37 37 37 41 40 42 47
  • P. zosteriformis
30 51 52 50 36 35 36 37 31 31 30 30 30 30 30 37 36 37 37 37 41 40 42 47
  • P. richardsonii
8 28 29 29 36 36 36 36 2 1 3 8 8 7 7 7 7 7 2 1 2 3 3 7 6 9 14
  • P. perfoliatus
8 28 29 27 35 35 35 35 2 1 3 8 8 7 7 7 7 7 2 1 2 3 3 7 6 9 14
  • P. alpinus
7 27 28 28 36 36 36 36 1 1 2 7 7 6 6 6 6 6 1 1 2 2 6 5 8 13
  • P. illinoensis
9 29 30 30 37 37 37 37 3 3 2 9 9 8 8 8 8 8 1 2 3 2 2 8 7 10 15
  • P. amplifolius
2 22 23 23 31 31 31 31 8 8 7 9 1 1 1 1 1 8 7 8 9 9 13 12 15 20
  • P. pulcher
2 22 23 23 31 31 31 31 8 8 7 9 1 1 1 1 1 8 7 8 9 9 13 12 15 20
  • P. epihydrus
1 21 22 22 30 30 30 30 7 7 6 8 1 1 7 6 7 8 8 12 11 14 19
  • P. confervoides
1 21 22 22 30 30 30 30 7 7 6 8 1 1 7 6 7 8 8 12 11 14 19
  • P. praelongus
1 21 22 22 30 30 30 30 7 7 6 8 1 1 7 6 7 8 8 12 11 14 19
  • P. oakesianus
1 21 22 22 30 30 30 30 7 7 6 8 1 1 7 6 7 8 8 12 11 14 19
  • P. natans
1 21 22 22 30 30 30 30 7 7 6 8 1 1 7 6 7 8 8 12 11 14 19
  • P. gramineus
8 28 29 29 37 37 37 37 2 2 1 1 8 8 7 7 7 7 7 1 2 3 3 7 6 9 14
  • P. crispus
7 27 28 28 36 36 36 36 1 1 2 7 7 6 6 6 6 6 1 1 2 2 6 5 8 13
  • P. robbinsii
8 28 29 29 37 37 37 37 2 2 1 3 8 8 7 7 7 7 7 2 1 3 3 7 6 9 14
  • P. spirillus
9 29 30 30 37 37 37 37 3 3 2 2 9 9 8 8 8 8 8 3 2 3 8 7 10 15
  • P. bicupulatus
9 29 30 30 37 37 37 37 3 3 2 2 9 9 8 8 8 8 8 3 2 3 8 7 10 15
  • S. filiformis
13 33 34 34 41 41 41 41 7 7 6 8 13 13 12 12 12 12 12 7 6 7 8 8 1 2 12
  • S. vaginata
12 32 33 33 40 40 40 40 6 6 5 7 12 12 11 11 11 11 11 6 5 6 7 7 1 3 11
  • S. pectinata
15 35 36 36 42 42 42 42 9 9 8 10 15 15 14 14 14 14 14 9 8 9 10 10 2 3 12
  • Z. palustris
20 40 41 41 47 47 47 47 14 14 13 15 20 20 19 19 19 19 19 14 13 14 15 15 12 11 12
  • B. atpB-rbcL-184
Species
  • P. foliosus
  • P. friesii
  • P. obtusifolius
  • P. subsibiricus
  • P. vaseyi
  • P. hillii
  • P. pusillus
  • P. strictifolius
  • P. zosteriformis
  • P. richardsonii
  • P. perfoliatus
  • P. alpinus
  • P. nodosus
  • P. illinoensis
  • P. amplifolius
  • P. pulcher
  • P. epihydrus
  • P. confervoides
  • P. praelongus
  • P. oakesianus
  • P. natans
  • P. gramineus
  • P. crispus
  • P. robbinsii
  • P. spirillus
  • P. bicupulatus
  • S. filiformis
  • S. vaginata
  • S. pectinata
  • Z. palustris
  • P. foliosus
1 1 17 18 1 17 17 19 18 18 17 19 20 21 21 18 20 25 21 21 21 22 20 56 57 75 75 66 62
  • P. friesii
1 18 19 2 18 18 20 19 19 18 20 21 22 22 19 21 26 22 22 22 23 21 57 58 76 76 67 63
  • P. obtusifolius
1 18 19 2 18 18 20 19 19 18 20 21 22 22 19 21 26 22 22 22 23 21 57 58 76 76 67 63
  • P. subsibiricus
17 18 18 1 18 2 6 6 5 9 10 10 10 3 8 12 8 8 7 9 6 42 44 64 64 56 55
  • P. vaseyi
18 19 19 1 19 1 1 3 7 7 6 10 11 11 11 4 9 13 9 9 8 10 7 43 45 65 65 57 56
  • P. hillii
1 2 2 18 19 18 18 20 19 19 18 20 21 22 22 19 21 26 22 22 22 21 21 57 58 76 76 67 63
  • P. pusillus
17 18 18 1 18 2 6 6 5 9 10 10 10 3 8 12 8 8 7 9 6 42 44 64 64 56 55
  • P. strictifolius
17 18 18 1 18 2 6 6 5 9 10 10 10 3 8 12 8 8 7 9 6 42 44 64 64 56 55
  • P. zosteriformis
19 20 20 2 3 20 2 2 8 8 7 11 12 12 12 5 10 14 10 10 9 11 8 42 44 66 66 58 57
  • P. richardsonii
18 19 19 6 7 19 6 6 8 5 5 6 12 12 7 12 16 12 12 11 13 9 48 49 68 68 60 56
  • P. perfoliatus
18 19 19 6 7 19 6 6 8 5 5 6 12 12 7 12 16 12 12 11 13 9 48 49 68 68 60 56
  • P. alpinus
17 18 18 5 6 18 5 5 7 5 5 7 8 12 12 6 11 15 11 11 10 12 8 45 46 65 65 57 56
  • P. nodosus
19 20 20 9 10 20 9 9 11 5 5 7 1 11 11 10 11 17 11 11 12 14 10 48 49 69 69 61 56
  • P. illinoensis
20 21 21 10 11 21 10 10 12 6 6 8 1 12 12 11 12 16 10 10 13 15 11 49 50 68 68 60 57
  • P. amplifolius
21 22 22 10 11 22 10 10 12 12 12 12 11 12 8 10 14 10 10 9 11 8 47 48 66 66 59 56
  • P. pulcher
21 22 22 10 11 22 10 10 12 12 12 12 11 12 8 10 14 10 10 9 11 8 47 48 66 66 59 56
  • P. epihydrus
18 19 19 3 4 19 3 3 5 7 7 6 10 11 8 8 6 10 6 6 5 7 4 41 42 61 61 54 53
  • P. confervoides
20 21 21 8 9 21 8 8 10 12 12 11 11 12 10 10 6 10 6 6 7 7 6 45 46 65 65 58 54
  • P. praelongus
25 26 26 12 13 26 12 12 14 16 16 15 17 16 14 14 10 10 6 6 11 11 10 47 48 66 66 59 57
  • P. oakesianus
21 22 22 8 9 22 8 8 10 12 12 11 11 10 10 10 6 6 6 7 9 6 43 44 62 62 55 54
  • P. natans
21 22 22 8 9 22 8 8 10 12 12 11 11 10 10 10 6 6 6 7 9 6 43 44 62 62 55 54
  • P. gramineus
21 22 22 7 8 22 7 7 9 11 11 10 12 13 9 9 5 7 11 7 7 7 5 42 43 60 60 53 55
  • P. crispus
22 23 23 9 10 21 9 9 11 13 13 12 14 15 11 11 7 7 11 9 9 7 5 46 47 63 63 56 55
  • P. robbinsii
20 21 21 6 7 21 6 6 8 9 9 8 10 11 8 8 4 6 10 6 6 5 5 43 44 61 61 54 52
  • P. spirillus
56 57 57 42 43 57 42 42 42 48 48 45 48 49 47 47 41 45 47 43 43 42 46 43 2 41 41 50 69
  • P. bicupulatus
57 58 58 44 45 58 44 44 44 49 49 46 49 50 48 48 42 46 48 44 44 43 47 44 2 41 41 50 69
  • S. filiformis
75 76 76 64 65 76 64 64 66 68 68 65 69 68 66 66 61 65 66 62 62 60 63 61 41 41 16 65
  • S. vaginata
75 76 76 64 65 76 64 64 66 68 68 65 69 68 66 66 61 65 66 62 62 60 63 61 41 41 16 65
  • S. pectinata
66 67 67 56 57 67 56 56 58 60 60 57 61 60 59 59 54 58 59 55 55 53 56 54 50 50 16 16 69
  • Z. palustris
62 63 63 55 56 63 55 55 57 56 56 56 56 57 56 56 53 54 57 54 54 55 55 52 69 69 65 65 69
  • C. ITS2-157

Distances: number of substitutions per site (Tamura and Nei, 1993)

13 resolved species 17 resolved species

23 resolved species (77%)

atpB-rbcL-184 ITS2

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SLIDE 10
  • Z. palustris
  • S. filiformis
  • S. pectinata
  • P. crispus
  • P. foliosus
  • Z. palustris
  • S. filiformis
  • S. pectinata
  • P. crispus
  • P. foliosus

THE DETECTED SPECIES WERE UNAMBIGUOUSLY RESOLVED BY THE SELECTED eDNA MARKERS

atpB-rbcL-184 ITS2

ML Fast Tree (Price et al., 2010)

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SLIDE 11

SELECTION OF THE SITE FOR THE EXPERIMENT

Grand River at CHARITABLE RESEARCH RESERVE (rare), Ontario

  • Easy to access: 30 km SW from Guelph, about 30 min drive
  • Two species of pondweeds (Potamogeton crispus and Stuckenia

pectinata) were collected during the ecological survey (Telfer et al., 2015)

The goal of our experiment was to detect the species of pondweeds where they were AT LEAST previously documented!

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SLIDE 12

THE WORKFLOW OF THE EXPERIMENT

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SLIDE 13
  • All three markers performed highly specifically and

consistently across the locations

  • ITS2-157 detected more species compared to atpB-rbcL

Abundance of reads after filtering Percent of reads hit the local reference library Number of pondweed species detected

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SLIDE 14

WHY REFERENCE LIBRARY MATTERS?

Incompleteness and conflicting taxonomy affect the results

Top Hit Identification Location Library eDNA Marker and Raw Data Treatment atpB-rbcL-117 atpB-rbcL-184 ITS2-157

Dereplicated Clustered Dereplicated Clustered Dereplicated Clustered

Potamogeton crispus

2

DS- POTAM

270 275

Gen Bank

275

Potamogeton foliosus

1

DS- POTAM

1,363 1,367 2

DS- POTAM

454 453 3

DS- POTAM

14,062 13,954 1,267 1,274

Potamogeton gayi

3

Gen Bank

13,938

Potamogeton pusillus

1

Gen Bank

1,367 2

Gen Bank

453 3

Gen Bank

1,274

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SLIDE 15

Top Hit Identification Location Library eDNA Marker and Raw Data Treatment atpB-rbcL-117 atpB-rbcL-184 ITS2-157

Dereplicated Clustered Dereplicated Clustered Dereplicated Clustered

Stuckenia filiformis

1

DS-POTAM

778

2

DS-POTAM

6,412

3

DS-POTAM

4,031 Stuckenia pectinata

1

DS-POTAM

47,979 49,141 191,594 180,965 9,263 9,267

Gen Bank

49,141 180,967 9,267

2

DS-POTAM

295,614 307,529 226,484 212,250 30,684 30,775

Gen Bank

307,779 212,272 30,775

3

DS-POTAM

329,810 335,372 344,475 324,822 34,610 34,639

Gen Bank

335,372 324,824 34,639

WHY RAW DATA TREATMENT MATTERS?

Analysis of dereplicated (=identical) sequences revealed a species,

  • therwise hidden in the post-clustering analysis
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SLIDE 16

NEGATIVES AND NON-TARGET DNA

Top Hit Identification Location Library eDNA Marker and Raw Data Treatment atpB-rbcL-117 atpB-rbcL-184 ITS2-157

Dereplicated Clustered Dereplicated Clustered Dereplicated Clustered

Stuckenia pectinata

PCR NEGATIVE DS- POTAM

12 12

Gen Bank

12

Panicum capillare

2

Gen Bank

34

Charophyta

1

Gen Bank

25

Cyanobacteria

1

Gen Bank

60 2

Gen Bank

13

Proteobacteria

DNA NEGATIVE Gen Bank

77 1

Gen Bank

229 2

Gen Bank

153 3

Gen Bank

40

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SLIDE 17

WE FOUND TWO SPECIES PREVIOUSLY DOCUMENTED …AND THREE MORE!

Species documented at the experimental site (Telfer et al., 2015):

  • Potamogeton crispus
  • Stuckenia pectinata

rare checklist (Jenna Quinn, rare, personal communication):

  • Potamogeton amplifolius*
  • Potamogeton crispus
  • Potamogeton pusillus**
  • Stuckenia pectinata

New to both previous reports:

  • Potamogeton foliosus
  • Stuckenia filiformis
  • Zannichellia palustris

* Potentially was not at the experimental site

** Potential misidentification of P. foliosus?...MK

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SLIDE 18

CONCLUSIONS

  • eDNA effectively detects different species of pondweeds in water

samples, revealing their potential under-estimated diversity in the aquatic communities

  • The developed protocol can be used for ecological surveys,

biomonitoring, and locating rare and protected species

  • Using both chloroplast and nuclear markers improves species

resolution among the selected species of pondweeds and increases reliability of the results

  • The results of eDNA detection strongly depend on the completeness

and accuracy of the reference libraries.

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SLIDE 19

Species at Risk Research Fund for Ontario (SARRFO) Ministry of Natural Resources

Alex Borisenko Nataly Ivanova Vasco Elbrecht Stephanie Pedersen Elizabeth Sears Jenna Quinn