Competitive interactions between non-native and native salmonids and their ecological consequences.

Similar documents
Jörgen I. Johnsson, coordinator Department of Biological and Environmental Sciences University of Gothenburg

niche requirements, interspecific

NINA Aquatic Research Station, Ims

RECREATIONAL PONDS AND LAKES

Hatcheries: Role in Restoration and Enhancement of Salmon Populations

Strategies for mitigating ecological effects of hatchery programs

The ecology of salmon and trout in lakes

FISHERIES BLUE MOUNTAINS ADAPTATION PARTNERSHIP

Fish Conservation and Management

Ecology of stream-rearing salmon and trout Part II

Notebooks or journals for drawing and taking notes

Ocean and Plume Science Management Uncertainties, Questions and Potential Actions (Work Group draft 11/27/13)

Chinook salmon (photo by Roger Tabor)

Brook Trout Life Cycle and Habitat

WFC 10 Wildlife Ecology & Conservation Nov. 29, Restoration Ecology: Rivers & Streams. Lisa Thompson. UC Cooperative Extension

Protect Our Reefs Grant Interim Report (October 1, 2008 March 31, 2009) Principal investigators: Donald C. Behringer and Mark J.

6/2/2014. Carps. Common Carp. Silver Carp. Rohu. Bighead Carp. Other introductions: Gourami Dojo Golden apple snail Pacu Mosquito fish

Council CNL(17)33. Annual Progress Report on Actions Taken Under the Implementation Plan for the Calendar Year EU - Denmark

Risk Evaluation of Norwegian Aquaculture and the new Traffic light system

How Marine-Derived Nutrients Benefit Both Natural and Model Stream Systems

Environment, Climate Change and Land Reform Committee. Environmental impacts of salmon farming. Written submission from Fisheries Management Scotland

Aquatic biodiversity conservation and the case of salmonid stocking: Identifying drivers for policy change

Todd N. Pearsons, Ph.D. Grant County PUD. Presented at the University of Washington

Michael Tehan, Assistant Regional Administrator, Interior Columbia Basin Office

The Effects of Stream Adjacent Logging on Downstream Populations of Coastal Cutthroat Trout

Groundfish Science Report Michelle McClure and John Stein. IEA Update. Cisco Werner and John Stein. September 15, 2011

Mark L. Botton and Robert E. Loveland. The Importance of Horseshoe Crabs in the Ecology of Delaware Bay: More than Just Bird Food?

Ecological interactions between parasites and wildlife

Two types of physical and biological standards are used to judge the performance of the Wheeler North Reef 1) Absolute standards are measured against

B. Disturbance and preda7on in fish

Yakima River Basin Coho Reintroduction Feasibility Study

Life Beyond the Spawning Grounds: Distribution & Food Web Relations of Herring & Forage Fishes in Puget Sound

RIVER CONONISH INVERTEBRATE SURVEY Dr Kjersti Birkeland

Population Structure

Final report on fish diet and stomach analyses

Fifty years ago, a single cod was large enough to feed a family of four or five. Today it is barely enough for one

The influence of Atlantic salmon (Salmo salar) and brown trout (Salmo trutta)on the breeding of the white-throated dipper (Cinclus cinclus)

Nearshore Ecology of Atlantic Salmon in the Gulf of Maine Region. Workshop 2: Bays and the Gulf of Maine

Booklet translated by SREJ at CSDC 1

Grande Ronde Basin Spring Chinook Salmon Captive Broodstock Program: F 1 Generation

Renseignements supplémentaires. Supplementary Information. Présentation du Ministère des Richesses naturelles de l Ontario

Fish Survey Report and Stocking Advice for Loch Milton. (Loch a Mhuilinn), May 2011

Wild Steelhead Coalition Richard Burge Conservation VP September 11, 2006

Compe&&on pp in text

Why the International Community Needs to Help Create Marine Reserves

The SONGS artificial reef mitigation project is linked to the adverse effects of the SONGS single pass seawater cooling system on the San Onofre kelp

Mid-Continent Ecology Division Jack Kelly Peder Yurista. University of WI - Superior

ELECTRO-FISHING REPORT 2016 UPPER TWEED

NEVADA DEPARTMENT OF WILDLIFE STATEWIDE SPORT FISHERIES MANAGEMENT

SALMON FACTS. Chinook Salmon. Oncorhynchus tshawytscha

Salmon Five Point Approach restoring salmon in England

Interactive effects of Russian olive and the common carp on linked stream-riparian food webs

Challenges in communicating uncertainty of production and timing forecasts to salmon fishery managers and the public

Life history patterns: many solutions to the same problem

1.What is a bull trout? 2.What is a metapopulation? 3.How do they go together?

B. Disturbance and preda7on in fish

ECOLOGY APRIL MR. SCHULLER

POLYCULTURE OF LARGEMOUTH BASS (Micropterus salmoides) WITH BLUE TILAPIA (Oreochromis aurea): USING TILAPIA PROGENY AS FORAGE

Whither the Hybrid Swarm? Stream environments segregate cutthroat and rainbow trout to control hybrid zone locations

NEVADA DEPARTMENT OF WILDLIFE STATEWIDE FISHERIES MANAGEMENT

Search for the missing sea otters

Untested Assumptions in Fisheries Management: the role of competition in Brook Trout declines?

Aquaculture, Introductions and Transfers and Transgenics Focus Area Report

Geology. Key Factors. Overfishing. Great Lakes Fishes. Historical Fishing. About 10,000 years since last glacial retreat very young ecologically

The Potential for Open Ocean. Zones from Global and National Perspectives

Salmon age and size at maturity: Patterns and processes

Introduction: JadEco, LLC PO BOX 445 Shannon, IL 61078

New New Zealand Mudsnail. New Zealand Mudsnail. Why you should care. How they got here and spread. What you can do SPECIES IN DEPTH

Trout stocking the science

Oregon Hatchery Research Center January 2014 David L. G. Noakes, Professor & Director

Aquatic Exotics In Wisconsin

Trends in salmon fisheries

Marine Food Webs and Fisheries

Historical Disturbances

Modes of prey detec-on by predators

Keuka Lake State of the Lake 2017

Benchmark Statement Respecting the Fish, Fish Habitat and Fisheries of Fish and Little Fish Lake, within the Taseko River Watershed.

Green crabs: invaders in the Great Marsh Featured scientist: Alyssa Novak from the Center for Coastal Studies/Boston University

WFC 50 California s Wild Vertebrates Jan. 11, Inland Waters (Lakes and Streams) Lisa Thompson

Homing and Straying, Part II Mechanisms of Homing: Imprinting, Genetics, and Pheromones

Spokane River Fish and Flows Recommendations and Rationale September Hal Beecher Washington Department of Fish and Wildlife

STREAM DRIFT. Much variation among taxa: Fraction of benthos drifting: Distance drifted? at any moment? over 24 hr period?

Old Stream is a highly productive cold water tributary to the Machias River located in Washington County, Maine. The Machias River contains a portion

Diet spectrum and preference of the invasive round goby (Neogobius melanostomus) in Flanders (North Belgium)

Ad Hoc Review Group IP(06)12 FINAL. Implementation Plan. European Union (Denmark)

Fish Tech Weekly Outline January 14-18

Colorado River near Parshall

Genome mapping in salmonid fish

Populations and Life Cycles. Hawaii s Freshwater Ecosystems

Big Spring Creek Habitat Enhancement and Fishery Management Plans

Council CNL(15)26. Annual Progress Report on Actions Taken Under Implementation Plans for the Calendar Year EU Spain (Navarra)

Development of wild fish surrogates for Upper Willamette River salmonids

Consumer Preferences, Ecolabels, and Effects of Negative Environmental Information By Xianwen Chen, Frode Alfnes and Kyrre Rickertsen

Council CNL(16)30. Annual Progress Report on Actions Taken Under the Implementation Plan for the Calendar Year EU - Spain (Navarra)

Mackerel and Herring - Competition or Coexistence?

STUDY PERFORMANCE REPORT

FISH 336 Introduction to Aquaculture

Background. Port Mouton Bay is an historically important habitat for lobsters, supporting generations of fishers

Genetic and ecological effects of salmon farming on wild salmon: modelling from experimental results

Compound Aqua feeds in a More Competitive Market: Alternative protein sources for a more sustainable future

Transcription:

Competitive interactions between non-native and native salmonids and their ecological consequences. Line Sundt-Hansen (NINA) Julien Cucherousset (Universite Paul Sabatier) Kjetil Hindar (NINA)

Introduction Invasive salmonids have been released intentionally or unintentionally by escapes from aquaculture for decades Native salmonid species are often in competition with nonnative species or non-native genotypes Non-native salmonids have reduced the growth and foraging rate of native salmonids (Korsu et al. 2010)

Background A competing species cannot invade an ecosystem unless it is sufficiently different in resource use from a native species Limiting similarity concept (MacArthur and Levins 1967)

Project Hypothesis Impacts are larger on native species and lower on recipient ecosystems when introducing the same species, but different genotypes. Eg. Farmed salmon vs. wild salmon The competitive effects are smaller and the ecosystem effects stronger when introducing different species, due to a lower level of niche overlap and a broader trophic niche

Research questions How will invasive species/genotypes perform relative to native species? Will invasive species and genotypes have an impact on growth and survival of native juvenile Atlantic salmon? Will invasive species in competition with native juvenile Atlantic salmon affect algae biomass and the presence of benthic invertebrates differently than wild salmon alone? Focus on the juvenile stage

NINA Research Station Ims

Semi-natural stream channel

Experiment Performance of invaders +BT +FS Effect on native species No fish +RT + Ecological impact: Benthic invertebrates Algae biomass Ecosystem

Experimental juvenile fish Atlantic salmon () Native Farmed Atlantic salmon (FS) Rainbow trout (RT) Brown trout (BT) Invading Native ECOSYSTEM

Study design N=5 + N=5+5 +FS N=5+5 +BT N=5+5 +RT N=5+5 No fish x 6

Assessments Performance of invaders (growth, mortality) Effect on native species (growth, mortality) Ecological impact: Benthic invertebrates Algae biomass 19 August 30 September 2014

RT significantly larger body mass Performance of invaders Inital mass No difference between BT, FS and

Condition factor RT significantly higher CF at start Not significant at termination

Experimental fish Specific growth rate (d -1 ) (body mass) Farmed salmon (FS) and brown trout (BT): Significantly higher growth rate than wild salmon () and rainbow trout (RT)

No significant differences between the experimental fish Survival

Specific growth rate (d -1 ), based on body mass Performance of Native species: Atlantic salmon No significant effect of competitor Significant effect of initial mass + + FS + BT + RT

Specific growth rate (d -1 ), based on body length * * Significant difference between + and +RT Significant effect of initial length + + FS + BT + RT

Survival No significant effect of treatment Wild Atlantic salmon performance + + FS + BT + RT

Benthic invertebrates Before start: 0-7 individuals in each sample (Chironomids) 1-10 snails (one channel 15-20 snails) At termination: Negligible: 0- few individuals Few invertebrates in substrate in stream channels Stomach content: Chironomids Snails

Pre-liminary algae biomass In general: low biomass of green algae and diatoms Green algae: Treatment +RT significantly higher biomass than in other fish treatments * * * Diatom Treatment +RT and NO FISH significantly lower biomass than in other fish treatments + + FS + BT + RT No fish + + FS + BT + RT No fish

Summary Performance of invasive species/genotypes: Farmed salmon (FS) and brown trout (BT) have a significantly better growth rate compared to wild salmon () and rainbow trout (RT) Effect of invasive species/genotypes on native salmon: No effect on survival Juvenile native salmon in competition with RT higher SGR (length) than alone in same number. Green alge biomass significantly higher biomass in treatment +RT

Concluding remarks Support to limiting niche theory? Larger size of RT, an advantage for the native salmon offspring RT were larger and had high CF at start; feeding motivation low? Or sufficiently different in niche use or size difference

Thank you! Thanks to: Eli Kvingedal Knut Andreas Eikeland Staff at NINA s Reseach station Ims

Performance of invaders and effects on native salmon (and a small piece of the food web) Line Sundt-Hansen Julien Cucherousset Kjetil Hindar

We hypothesized that impacts are larger on native species and lower on recipient ecosystems when introducing the same species, but different phenotypes. We then hypothesized that the competitive effects are smaller and the ecosystem effects stronger when introducing different species, due to a lower level of niche overlap and a broader trophic niche, respectively

Aim of study hypothesis Will invasive species/groups have an impact on growth and survival of wild salmon parr? How will invasive species perform relative to native species? Will invasive species in competition with wild salmon parr affect the food web differently than wild salmon alone? Focus on the juvenile stage which is particularly vulnerable

NINA Ims Research Station

Task 1.2 and 2.2: Exp.1 Semi-natural stream channels (2014) Experimental juvenile fish: Wild Atlantic salmon () Farmed Atlantic salmon (FS) Brown trout (BT) Rainbow trout (RT) +RT +BT + +FS ASSESSMENTS: Performance of invaders (growth, mortality) Effect on native species (growth, mortality) Effect of competition on ecosystem: Benthic invertebrates Primary production Diatomes Ecosystem

Experiment I: initiated 19 August; terminated 29-30 September 2014

Species Inital length (mm) ± SD Inital body mass (g) ± SD Condition factor± SD Brown trout 72.65 ± 5.7 4.63 ± 1.06 1.19 ± 0.06 Farmed salmon 72.58 ± 6.0 4.69 ± 1.21 1.20 ± 0.07 Rainbow trout 95.14 ± 9.1 12.65 ± 3.03 1.45 ± 0.22 Wild salmon 69.56 ± 5.9 4.55 ± 1.25 1.32 ± 0.08

Inital and final mass

Experimental fish Specific growth rate (d -1 ) (SGR.W) BT significantly different from RT, FS significantly different from RT, RT significantly different from BT,FS significantly different from FS,RT

Different species growth rate Significant effect of initial mass In rainbow trout and brown trout,

Survival

Wild Atlantic salmon performance Spesific growth rate (d -1 )

Wild Atlantic salmon performance

Survival Wild Atlantic salmon performance

Algea growth

Surber samples Few invertebrates in substrate in stream channels Before start: 0-7 individuals in each sample 1-10 snails (one channel 15-20 snails) At termination: Negligible: 0- few individuals Stomach content: Chironomids Snails

Summary No effect of presence of other species and genotypes on wild salmon growth and survival

Previous study

Survival and growth: stream channels Imsa Aquage early juvenile stage; n swim up High dens Low dens High dens Low dens Allopatry Allopatry Sympatry Sympatry Substitutive design Density equal effect on growth for farmed and wild offspring No effect of farmed fry on growth of wild fry Reduced survival of wild fry when in sympatry with farmed fry

River park 2015