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Three lamprey eDNA field studies: what we learned by applying eDNA methodology Carl Ostberg Western Fisheries Research Center, USGS

Three lamprey eDNA field studies: what we learned by applying … 5... · 2018. 3. 5. · eDNA water collections (25 sites) Temporal distribution of water collections 2014 Jul Aug

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Page 1: Three lamprey eDNA field studies: what we learned by applying … 5... · 2018. 3. 5. · eDNA water collections (25 sites) Temporal distribution of water collections 2014 Jul Aug

Three lamprey eDNA field studies: what we learned by applying eDNA methodology

Carl OstbergWestern Fisheries Research Center, USGS

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Overview

Three lamprey field studies1. Tracking colonization in the Elwha River following 

dam removal2. Distribution and seasonal differences in eDNA

across Puget Sound watersheds3. Spatial distribution and occupancy in Chehalis 

River tributaries

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eDNA method

Filtration

Quantitative PCR (typically 3 replicates)

Extract DNA

3 replicate water samples/site (+ Negative controls)

1L 1L 1L

0 1 2 3 4 5 6 7 8 9Number positive qPCRs Quantify DNA copy #

Results

? ? ? ? ? ? ? ? ? Target species detected?

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Study 1: Using eDNA to track recolonization and dispersal of fishes 

following dam removal on the Elwha River, Olympic National Park, Washington

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eDNA is a good method for monitoring recolonization in backcountry

Removed April 2012

Removed August 2014

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Objective

Use spatial and temporal sampling of eDNA as a means for monitoring:• Spatial extent of recolonization by native species • Dispersal of non‐native Brook Trout

Chinook

Steelhead

Coho Pink Chum

Sockeye Coastal Cutthroat

Pacific Lamprey

Jeremy Monroe

Bull Trout

USFWS

Lampetra spp

Mike Hayes

Native anadromous species

Brook TroutNon‐native

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1

2

34

5

10

6

78 9

1112

1314 15

16

17

1819

202122

23

2425

Spatial distribution of Elwha eDNA water collections (25 sites)

Temporal distribution of water collections

2014 Jul Aug Sep Oct Nov Dec

2015 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

2016 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

2017 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

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2014 2015 2016

Jul

Sep

Nov

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov Jan

Feb

Mar

Apr

May

Jun

1 X X X X X X

23456 X X X X X X X X

7 X X X

8 X X X X X X X X X X

9 X X X X X X

10 X

11 X X

12 X X X X X X X X

13 X X X X X X X X X X X X X X X

14 X X X X X X X X

15 X X X X X X X X

16‐25 X X X X X X X X X X X X X X X X

1

2

34

5

10

6

78 9

1112

1314 15

16

17

1819

202122

23

24250 1 2 3 4 5 6 7 8 9

Number positive qPCRs (out of 9)

x Not sampled

Pacific Lamprey eDNA detection

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2014 2015 2016

Jul

Sep

Nov

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov Jan

Feb

Mar

Apr

May

Jun

1 X X X X X X

23456 X X X X X X X X

7 X X X

8 X X X X X X X X X X

9 X X X X X X

10 X

11 X X

12 X X X X X X X X

13 X X X X X X X X X X X X X X X

14 X X X X X X X X

15 X X X X X X X X

16‐25 X X X X X X X X X X X X X X X X

1

2

34

5

10

6

78 9

1112

1314 15

16

17

1819

202122

23

24250 1 2 3 4 5 6 7 8 9

Number positive qPCRs (out of 9)

x Not sampled

eDNA detections increase over time

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2014 2015 2016

Jul

Sep

Nov

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov Jan

Feb

Mar

Apr

May

Jun

1 X X X X X X

23456 X X X X X X X X

7 X X X

8 X X X X X X X X X X

9 X X X X X X

10 X

11 X X

12 X X X X X X X X

13 X X X X X X X X X X X X X X X

14 X X X X X X X X

15 X X X X X X X X

16‐25 X X X X X X X X X X X X X X X X

1

2

34

5

10

6

78 9

1112

1314 15

16

17

1819

202122

23

2425

• Detections progress upstream over time

0 1 2 3 4 5 6 7 8 9

Number positive qPCRs (out of 9)

x Not sampled

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2014 2015 2016

Jul

Sep

Nov

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov Jan

Feb

Mar

Apr

May

Jun

1 X X X X X X

23456 X X X X X X X X

7 X X X

8 X X X X X X X X X X

9 X X X X X X

10 X

11 X X

12 X X X X X X X X

13 X X X X X X X X X X X X X X X

14 X X X X X X X X

15 X X X X X X X X

16‐25 X X X X X X X X X X X X X X X X

1

2

34

5

10

6

78 9

1112

1314 15

16

17

1819

202122

23

2425

• Single detections interpreted with caution

0 1 2 3 4 5 6 7 8 9

Number positive qPCRs (out of 9)

x Not sampled

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2014 2015 2016

Jul

Sep

Nov

Mar

Apr

May

Jun

Jul

Aug

Sep

Oct

Nov Jan

Feb

Mar

Apr

May

Jun

1 X X X X X X

23456 X X X X X X X X

7 X X X

8 X X X X X X X X X X

9 X X X X X X

10 X

11 X X

12 X X X X X X X X

13 X X X X X X X X X X X X X X X

14 X X X X X X X X

15 X X X X X X X X

16‐25 X X X X X X X X X X X X X X X X

1

2

34

5

10

6

78 9

1112

1314 15

16

17

1819

202122

23

2425

• Detections differ across months

0 1 2 3 4 5 6 7 8 9

Number positive qPCRs (out of 9)

x Not sampled

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Study 2: Distribution and seasonal differences in Pacific Lamprey and Lampetra spp eDNA across 18 Puget Sound watersheds

Study questions:1. How well does eDNA reflect 

known species distributions?

2. Are there seasonal differences in detection?

Sampling:Fall: October 9 – November 13, 2014Spring: May 6 – June 30, 2015, 

Manuscript in review

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Pacific Lamprey known occurrence• most data are from 2011

eDNA detected

Not present or eDNA not detected

• Application of eDNA replicated the known Pacific Lamprey distribution 

How well does eDNA reflect Pacific Lamprey distribution?

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1

10

100

1000

1

10

100

1,000

10,000

100,000

Flow

 rate (m

3 /s)

Pacific Lam

prey eDN

Amean 

copy no./L

Are there seasonal differences in eDNA detection?

• eDNA concentration higher in spring (better detection)• 14 streams positive in spring, 5 streams positive in fall

• False negative results for 9 streams

eDNA fall eDNA spring stream flow fall stream flow spring

Pacific Lamprey

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1

10

100

1000

1

10

100

1,000

10,000

100,000

Flow

 rate (m

3 /s)

Pacific Lam

prey eDN

Amean 

copy no./L

Are there seasonal differences in eDNA detection?

• Possible causes for lower detection in fall:• Flow rate• Life history

eDNA fall eDNA spring stream flow fall stream flow spring

Pacific Lamprey

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Study 3: Assessing the spatial distribution and occupancy of larval lamprey in Chehalis River tributaries

Black River (2015)

Skookumchuck River(2015)

Newaukum River(2015)

Wynoochee River (2017)Wishkah River 

(2017)

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• Evaluate performance of eDNA for detecting Pacific Lamprey and Lampetra spp compared to electrofishing.

• Determine if eDNA quantity is distributed differently for Pacific Lamprey and Lampetra spp within tributaries.

• Apply eDNA to an occupancy modeling framework

Objectives

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2015 sampling (Black, Skookumchuck, Newaukum)Target larval habitat (10 sites/tributary)

Patch size = 50 meters• e‐fishing (late Sep – early Oct, 2015)• eDNA sampling (Oct 20 – 21, 2015)• Caveats

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Pacific Lamprey: electrofishing vs. eDNA

Pacific Lamprey detections Electrofishing and eDNA

eDNA only 

Electrofishing only 

No detect by either method

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0

20,000

40,000

60,000

5 10 15 20 25 30 35 40

eDNA copy no./L

Distance from Chehalis River (rkm)

Lampetra spp, Skookumchuck River

0

1,000

2,000

3,000

4,000

5 10 15 20 25 30 35 40

eDNAcopy no./L

Distance from Chehalis River (rkm)

Pacific Lamprey, Skookumchuck River

Is eDNA quantity distributed differently for Pacific Lamprey and Lampetra spp within tributaries?

R2 = 0.715F = 20.05, P < 0.005

R2 = 0.061F = 0.522, ns

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• Combined temporal and spatial sampling• Allowed colonization to be tracked upstream over time.• Detections increased over time

• Single detections are interpreted with caution • replicated results provide confidence

• Seasonal differences in eDNA detection• Higher in spring/summer; lower in fall/winter

• Stream flow• Life history events

• eDNA accurately identifies species distributions

• eDNA performs comparably to electrofishing for identifying occupancy

• eDNA concentrations may inform on relative abundance/biomass• Further studies required

Lessons learned – summary

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Acknowledgements

USGS NPSMarshal Hoy Sam BrenkmanDorothy ChaseJeff Duda USFWSMike Hayes Jeff Jolley (now with USGS)

Carrie Cook‐TaborNOAA Judith BarkstedtGeorge Pess

LEKTMike McHenry

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Pacific Lamprey assay primer and probe sites are conserved among:• Vancouver Lamprey (E. macrostomus)• Miller Lake Lamprey (E. minimus)• Klamath Lamprey (E. similis)• Pit‐Klamath Brook Lamprey (E. lethophagus)

• forward primer has one mismatch with Pit‐Klamath Brook Lamprey

• Lampetra spp assay primer and probe sites are conserved among:• L. ayresii, L. richardsoni, L. pacifica, and L. hubbsi, although the assay may 

have limited or no detectability of Lampetra spp in certain geographic locations. 

• North Fork Siuslaw River, OR, Hunter Creek, CA, McGarvey Creek, CA, Kelsey Creek, CA, and Mark West Creek, CA

• Boguski et al. (2012) suggested the Lampetra spp in Siuslaw River, Kelsey Creek, and Mark West Creek could represent cryptic species. 

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Lampetra spp eDNA assay

Figure adapted from Boguski et al. 2012, Journal of Fish Biology 81:1891‐1914

Big River (1/4)

NF Siuslaw (5/5)

Hunter Ck (5/5)McGarvey Ck (5/5)

Kelsey Ck (4/4)Mark West Ck (4/4)

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Lampetra distribution

• Agreement between eDNA and fish traps for 17/18 locations

• Lampetra eDNA detected in one additional stream

Lampetra

Mike Hayes

Lampetra known occurrenceeDNA detectedNot present or eDNA not detected

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1

10

100

1000

1

10

100

1,000

10,000

100,000

1,000,000

Flow

 rate (m

3 /s)

LampetraeD

NAmean copy 

no./L

Seasonal difference in eDNA abundance

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Lampetra spp detections Electrofishing and eDNA detect

eDNA only detect

Electrofishing only detect

Not detected by either method

Lampetra spp: electrofishing vs. eDNA

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Linear regression: eDNA concentration on distance• Ho: slope is not different from zero

Distribution of Pacific Lamprey and Lampetra spp eDNA What do eDNA concentrations tell us?

110100

1,00010,000100,000

15 20 25 30 35 40 45 50 55 60Mean eD

NAcopy no./L

Distance from Chehalis River (rkm)

South Fork Newaukum River (8 sites)

Pacific Lamprey  Lampetra sppR2 = 0.436  R2 = 0.007F = 4.63, P = 0.075 (DF = 1, 6) F = 0.04, ns (DF = 1, 6)