Aquatic Invasive Species in the Upper Great Plains
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Transcript Aquatic Invasive Species in the Upper Great Plains
Aquatic Invasive Species in the
Upper Great Plains
Part I: Introduction to AIS
Aquatic invasive species (AIS)
Aquatic
Adapted to habitats
regularly or permanently
inundated (lakes, rivers,
wetlands)
Invasive Species
Non-native species that spread
rapidly, outcompete native species,
and cause harm (ecological,
economic, or social)
AIS characteristics
Not all non-native species are invasive
Not all invasive species can establish in a given area
Often difficult to predict effects of an AIS in an area
Usually difficult or impossible to eradicate once established
Also called Aquatic Nuisance Species (ANS) in some programs
Potential pathways for AIS spread
Recreation
Watercraft movement
Hunting and angling
equipment
Live bait releases
Float planes
Consumer
Aquarium releases
Water garden escapements
Industry
Aquaculture escapements
Live food trade
Internet sales
Industrial equipment
Shipping
Natural
Inter-connected waterways
Wildlife migrations
Why care about AIS?
Stable natural ecosystems support human development
AIS threaten this equilibrium:
Biodiversity
Recreation
Infrastructure
Human health
Some AIS displace native species
Some AIS can affect water quality
Examples of AIS
Zebra mussels
Quagga mussels
Asian carp (Invasive carp)
Eurasian watermilfoil
Curlyleaf pondweed
Viral hemorrhagic septicemia (VHS)
Zebra mussels
Adults:
Triangular or D-shaped
Up to 2 inches in length
Alternating bands (zebra)
Byssal threads help attach to
hard substrates
Siphons pump water
Larvae (veligers):
Microscopic
Free-floating (planktonic)
2 weeks to 3 months to settle
Byssal threads
Quagga mussels
Similar in appearance
Slightly larger
Thinner shell
Rounder shape
Cannot stand on side
Rings instead of zig-zags
Veliger stage similar
Higher tolerances
Found deeper
Travel farther
ZM/QM impacts
Ecosystem
Filter feeding
Bioaccumulation
Attachment
Recreation
Reduce populations
Sharp shells
Industry
Attachment
Water quality
Cost increases
Consumers
Cost increases
Water availability
Zebra mussels in El Dorado Reservoir, Kansas
Zebra mussels clog pipes
ZM/QM spread
ZM/QM pathways of spread
Downstream – veliger drift
Across land – by humans
In water (veligers)
Fouled equipment
Zebra mussels on anchor
Zebra mussels on buoy chain
Water may contain veligers
Asian carp
Bighead carp
Four species:
Black carp – up to 80 inches and 155
pounds, large scales
Grass carp – up to 60 inches and 100
pounds, large scales
Bighead carp – up to 51 inches and 110
pounds, fine scales, down-turned eyes
Silver carp – up to 51 inches and 77
pounds, fine scales, down-turned eyes
Silver carp
Grass carp
“Invasive carp” alternate term
Bighead carp
Asian carp impacts
Feeding behaviors (vary)
Black carp - mollusks
Grass carp – vegetation
Bighead carp – filter feeding
Silver carp – filter feeding
Bighead carp mouth
Silver carp jumping tendency
Grass carp
Jumping silver carp in the James River, SD
Asian carp pathways for spread
Originally imported for aquaculture
Bighead and silver – algae control
Grass – vegetation
Black – snails (trematodes)
Escapement
Bait bucket transfers
Bighead carp
Native gizzard shad
Silver carp
Eurasian watermilfoil
Widespread invasive plant used in
aquariums and water gardens
Difficult to distinguish from native
milfoils
4 leaves whorled around a hollow stem
At least 14 leaflet pairs
Typically found in 1 to 15 feet of water
Close-up of Eurasian watermilfoil
Eurasian watermilfoil
Forms a dense canopy at the water's surface
Decreases native plant and animal diversity
Impedes recreational activities
Dense mat of Eurasian watermilfoil
Eurasian watermilfoil
Natural spread
Downstream drift
Waterfowl
Human spread
Fragments on equipment
Vegetation on a propeller
Eurasian watermilfoil in the Sheyenne River, ND
Curlyleaf pondweed
Distinguished from native pondweeds
Lasagna noodle-shaped leaves
Fine serrations on leaf margins
Typically found in 3 to 6 feet of water
Finely serrated leaf
Native pondweed
Curlyleaf pondweed from North Dakota
Curlyleaf pondweed
Curlyleaf pondweed
Quickly forms dense mats on or near surface
Shades out native aquatic plants
Impedes recreation
Mid-summer die-offs can trigger fish kills
Curlyleaf pondweed in Raleigh Reservoir, ND
Close-up of curlyleaf pondweed
Curlyleaf pondweed
Natural spread
Downstream drift
Waterfowl
Human spread
Fragments on equipment
Aquatic vegetation on boat and trailer
Viral hemorrhagic septicemia (VHS)
Viral infection that can cause many symptoms and lead to death
Hemorrhaging in eyes, skin, gills, base of fins, internal organs
Darkening of skin
Bulging eyes
Bloated abdomens
Lethargy
Pale gills
Loss of osmotic function
VHS impacts
Can impact a variety of freshwater species
Many more species can act as carriers
Has led to large fish kills in isolated areas
VHS pathways of spread
Natural
Downstream drift of water
Swimming of infected fish
Human
Transferring infected fish (stocking or bait)
Contaminated gear
Contaminated water
Preventing the spread
Message varies but steps are similar:
Clean – inspect equipment and remove plants, animals, and mud
before leaving water access site
Drain – remove all water before leaving water access site
Dry – allow to dry completely or disinfect using approved method
(hot water, bleach, vinegar, salt, freezing, etc.)
Don’t dump bait – dispose of unused bait in trash or on land
Don’t release pets and plants into the wild
Goal is to prevent movement of water and organisms
Prevention is critical
END OF PRESENTATION
30 minutes available for a question and answer session
Aquatic Invasive Species in the
Upper Great Plains
Part II: Program implementation and considerations
AIS management
Factors affecting AIS distribution
Environmental tolerances
Movement constraints
Ecosystem connectivity
Do not adhere to social boundaries
Many watersheds are shared by multiple jurisdictions
Red River
James River
Rainy Lake
AIS management
Recreational boaters are becoming increasingly mobile
Fishing is “big business” for all 4 jurisdictions
Anglers seek a wide variety of opportunities
Closed fishing seasons in one jurisdiction may drive interstate travel
Internet forums allow for anglers to chase “a hot bite”
2012 inspection
results
Boaters travel
from many
places to fish in
Manitoba
Collaborative AIS management
Constituent “Buy-in”
Similar regulations in the region would cause less confusion
for user groups
Similar messaging in the region would prevent “mixedmessages” from agencies working towards the same goals
Clean, Drain, Dry
Inspect, Remove, Drain
Clean, Drain, Dispose
Clean, Drain, Dry, Dispose
Collaborative AIS management
A holistic, regional or eco-region approach to AIS management
may be the best
Examples of successful collaborations:
Pacific Northwest Economic Region (PNWER)
Western Invasive Species Collaborative Agreement
Invasive Mussel Prevention Framework
Mussel Defense Framework funding secured
Western Regional Panel on ANS Building Consensus
Uniform waterbody classification system
Model legislation for mandatory boat inspection programs
Finalizing model regulations for boat inspection programs
AIS program components
Outreach and education
Sampling and monitoring
Management and control
Research
Outreach and education
Goals are multi-faceted:
What AIS are and identification
Species impacts
Actions to prevent the spread
Relevant regulations
Outcomes:
Public awareness
Actions to prevent spread
Regulation compliance
Support of AIS program
Outreach and education
Multi-media strategies
Traditional media
Digital advertising
Signage
Printed literature
Social media
Giveaway items
Personal contacts
Repeated exposures
Highlight select species
Outreach and education
Similarities among jurisdictions
Spend a significant portion of resources on outreach
Feel that outreach and education efforts are important
Use a variety of media to convey messages
Goals are similar
Differences across jurisdictions
Slogans vary slightly
Each has their own branding
Variability in available resources
Sampling and monitoring
Early detection sampling
Find new populations
Techniques vary by species
Focused during peak season
Early detection use
Regular usage
High-risk waters
Many waters
eDNA sampling
Plankton tow
Sampling and monitoring
Long-term monitoring
Keep track of populations
Techniques vary by species
Standard intervals
Monitoring use
Special use
Infested waters
Select waters
Lake Winnipeg zebra mussel monitoring structures
Monitoring vegetation and invertebrates
Sampling and monitoring
Similarities among jurisdictions
Most feel this is a very important component of the program
Relatively small amount of resources required (20% or less)
Utilize early detection and long-term monitoring
Conduct species-specific and general lake sampling
Differences across jurisdictions
Some jurisdictions utilize private entities – leverages resources
Some jurisdictions have dedicated staff
Management and control
Regulations
Prevent new populations AND contain existing populations
Enforce good habits (Clean, Drain, Dry)
Target other harmful actions (releasing pets)
Law enforcement work with AIS staff to
identify needs and ensure compliance
Management and control
Prevention
Outreach/education very effective
Examples of other efforts:
Mandatory watercraft inspections
Hatchery biosecurity protocols
Bait vendor inspections
Agency disinfection protocols
Common carp barrier
Compliance is key
Boat decontamination in Manitoba
Management and control
Rapid response
Prevent AIS from establishing
Plans make response more effective
Eradication or control actions – based on goal
Interjurisdictional
Response varies
Rapid response training exercise for Asian carp in Illinois
Management and control
Control
Mitigate for impacts
Reduce numbers, not eliminate
Delay establishment
Sections of a water or infrastructure
Treating a cove with copper sulfate to delay zebra mussel spread
Management and control
Eradication
Eliminate population
Many factors affect success
Whole-system
Special scenarios
Asian carp were eradicated from Lake Yankton, SD in 2014
Management and control
Similarities among jurisdictions
Regulations regarding bait, bait water, draining water, possession
of live AIS, releasing organisms, equipment free of AIS
Internal agency protocols to prevent AIS spread
Differences across jurisdictions
In MN and MB: illegal to posses dead AIS, mandatory inspections
In ND: must remove vegetation
Attempted eradications in MB and MN for zebra mussels
Attempted control in MN for two species of plants
Research
Uses in ANS prevention
Researching AIS detection
Identify AIS of concern
Develop sampling methods
Identify management tools
Areas of research
Biology
Ecology
Impacts
Disinfection/eradication
techniques
Pathways of spread
Detection techniques
Control methods
Effective outreach strategies
Research
Emerging tools and ideas
Research advancement
Example 1: eDNA
Advances in technique
Potential for quantification
New marker developments
Example 2: CRISPR Cas-9
Gene-drive technology
All offspring inherit traits
Pros and cons
Processing eDNA samples
Research
Ongoing research within jurisdictions
MN – partners with MN AIS Research Center (30+ projects)
Identified research needs
Feasible and effective control/eradication techniques
Impacts – ecological, sociological, and economical
Effective outreach tools
More effective monitoring tools
Program implementation
There are many factors that will impact an AIS program
Ecological
Economical
Social
Regulatory
Fiscal
Ecological factors
Which species are in the jurisdiction and which are in nearby
jurisdictions?
Of those which can overwinter and become invasive?
What are their potential impacts
Species-specific
Prediction difficult
Curlyleaf pondweed in North Dakota
Economical considerations
Industry as a pathway
Bring in novel species
Sell across landscape
Move water and AIS
Not always regulated
Impacts to industry
Equipment fouling
Water quality
Costs to mitigate
Regulations
Purple loosestrife was introduced as an ornamental
Social considerations
Recreation as a pathway
Direct contact with water – boaters, anglers, waterfowl hunters
Indirect pathways – aquariums, water gardens, pets
Impacts to recreation
Ecosystem effects
Harm to humans
Aesthetics
Silver carp jumping in South Dakota
Regulatory considerations
Social acceptance and compliance
Balance resource needs and public desires
Acceptance may affect compliance
Ease of compliance and enforceability
Authority/mechanism for implementation
Limited statutory authority
Collaboration with regulating agencies
Processes for implementing rules
Water uses must be considered
Fiscal considerations
Sources for funding
Natural resource agencies – license fees
Special use fees – boaters
Legislative apportionments
Prioritizing resource allocation
Funding source stipulations
Other considerations
Funding sources and stipulations may affect how resources are allocated in AIS programs
Inter-jurisdictional considerations
Protecting individual boundaries
AIS management on eco-region scale
AIS management within jurisdiction
Strength through collaboration
Inter-jurisdictional considerations
Overcoming discrepancies
Finding commonalities
Goals
Program components
Great Lakes region; federal
Prioritizing areas
Scientific research
Population-level approach
Kansas; state
Streamlining
Similar messaging
Customer service
Working across agencies and jurisdictions
Inter-jurisdictional considerations
How legislation fits in:
Many user groups affected
Direct resource users – boaters, anglers, hunters
Indirect resource users – drinking water, power generation
Industry – rely on water for production or can impact resource
Prevention now will save resources
Costs to mitigate are very high
Eradication is very expensive if even possible
Legislation affects water resources
Water movement
Equipment movement
Industries – water or organisms
Contact information
Manitoba: Jeff Long, MB Sustainable Development
(204) 945-7792 or [email protected]
Minnesota: Heidi Wolf, MN DNR
(651) 259-5152 or [email protected]
OR Becca Nash, MN AIS Research Center
(612) 624-7785 or [email protected]
North Dakota: Jessica Howell, ND Game and Fish
(701) 368-8368 or [email protected]
South Dakota: Mike Smith, SD Game, Fish, and Parks
(605) 223-7706 or [email protected]