Modeling water and small particle residence times in two ...
Transcript of Modeling water and small particle residence times in two ...
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Modeling water and small particle residence times in two rearing units used for intensive
culture of steelhead trout Oncorhynchus mykiss in Idaho
Kelly Stockton1, Christine Moffitt1, Tim Allan2, Barnaby Watten3, Brian Vinci4
1USGS: Fish and Wildlife Cooperative Research Unit, University of Idaho 2University of Virginia, 3USGS:
Leetown Science Center, 4Freshwater Institute
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Burrows Pond (BP)
Drain
Drain Center Wall
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DrainDrain Drain Drain
Mixed-Cell Raceway (MCR)
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Velocity Profiles• Velocity measurements collected with a Sontek/YSI
Acoustic Doppler Velocimeter
• Cross-section profiles were measured at 0.3046 and 0.6096 m from surface, in 0.3046 m intervals
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Fig. 4: MCR velocity contours and vectors at 0.6096 m depth.
Fig. 3: BP velocity contours and vectors at 0.6096 m depth.
Velocity Profiles
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Hydraulic Residence Time• Salt tracer added and measured every minute
at tank discharge
• Concentration normalized and depletion curve analyzed using 95% of the curve to remove the effect of long tails (Levenspiel1979)
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Hydraulic Residence Time
• BP and MCR
– Mixed
– Residence time close to ideal
– Few stagnant regions
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Particle Removal Efficiency: Bead test• Plastic beads simulate NZMS and infested feces
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Particle Removal• MCR: 99% Removal Efficiency
• BP: 6.8% Removal Efficiency
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Conclusion• MCR is a better system for rearing fish
• NZMS
– Scouring velocities:
• BP: 8.1 mm
• MCR: 17.03 mm
– Velocities: benthic shear stress:
• ~25 m/s needed to move NZMS
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Biosecurity Framework and Methods to Protect Aquaculture
Facilities against Invasive Mollusks
Kelly Stockton1
Christine M. Moffitt2
1Idaho Cooperative Fish and Wildlife Research Unit, University of Idaho2US Geological Survey, Department of Fish and Wildlife, University of Idaho
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Aquaculture Facilities and Invasives
• Often constant temperatures
• Constant flows
• Nutrients available
• Transport fish
• Near fishing areas, wildlife reserves and public access
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New Zealand mudsnail(Potamopyrgus antipodarium)
• Small→gear
• Operculum
• Parthenogenic reproduction
• High densities
• Shells→Salmonid digestion
High Densities
Operculum
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Risk Management• State, provincial, national regulations require
management of invasive species
• HACCP used in many facilities
• Applicable to any operation or species
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Reducing and Managing Hazards of Invasive Mollusks in Aquaculture
• Need effective validated monitoring, disinfection and removal tools
• Inconsistent results from multiple, often limited trials
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Hatchery Managers Need GuidanceRisk
Assessment
Monitoring
DisinfectionRisk
Management
Removal Tools
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Biosecurity Framework and Methods to Protect Aquaculture Facilities
• Evaluate risks and consequences with a framework and decision tree
• Assess the validity of monitoring, disinfection and removal tools
SpringWell
Stream
Effluent
Hatchery
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Assessing Tools• Literature search
– Peer review, theses, reports, personal communications
• Ranked criteria: low, medium, high
• Certainty of results analyzed
• Traditional decision treeprocess
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RecommendationsAssess Critical Control Points Use tools to lower risk
Choices/ConstraintsPrevention Status Quo Manage Eradicate
Status of FacilityNot Infested Infested
Risk PotentialProbability of Establishment Consequences of Establishment
Risk Assessment and Management
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Probability of EstablishmentPathway Evaluation
1. Assessment of Establishment
• Likelihood of pathways
2. Entry Potential
• Likelihood of organism surviving transit in pathway
3. Colonization Potential
• Likelihood of environmental characteristics
4. Passive Spread Potential
• Likelihood of spreading to area
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1. Assessment of Establishment and 2. Entry Potential
Pathway
Is your facility affected by
this pathway (yes=1, no=0)
Likelihood of organism
surviving transit in
pathway to area*
Multiply
column
B*C
Anglers
Aquarium trade
Ballast water
Birds and mammals
Boaters
Effluent pond
Field crews
Fish collection
Fish transport
Open water source
Other recreationalists
Visitors
Total Risk for 1&2:
* Determine likelihood based on areas climate or regulations. Ranking: 6= uncertain,
5=very high, 4=high, 3=medium, 2=low, 1= very low
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3. Colonization Potential• Stream – Water Body Characteristics
– Flow rate, depth, stream order, elevation, habitat type, substrate type, connectivity
• Water Quality Characteristics
– Season, temperature, specific conductivity, calcium concentration, pH, phosphorus ratios, salinity
• Human Mediated Characteristics
– Disturbance/pollution, angling/stocking, birds
Low Medium High Source
Flow rate >100 cm/sec 70-100 cm/sec <70 cm/sec Holomuzki and Biggs 1999
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Certainty Analysis
• All characteristics analyzed
– Lab/field
– Source type
– Endpoint
– Temperature
– Salinity
– Source population
– Location
– pH
– Calculated/ given
– NZMS or other
Source
Lab/
field
Source
type Temp.
Source
population Location
Calculated
/given
Flow Rate
Holomuzki and Biggs
1999 lab
peer
review 19
freshwater
river
New
Zealand calculated
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3. Colonization PotentialCharacteristic Ranking Rank # Certainty * Resulting Risk (C*D)StreamFlow Rate
Flow rate- expansion rate
Flow-upstream spread rate
Depth
Stream Order
Elevation
Light Intensity
Habitat type
Substrate type
Connectivity to downstream pop (fish movement)
Average of Stream :
Water QualitySeason
Temperature (max.)a
Optimal Temperature
Temperature (min)a,b
Specific Conductivity
Calcium Concentrationd
pH
Phosphorus ratios
Salinity
Average of Water Quality:
Human MediatedDisturbance
Sediment pollution
Estrogen pollution
Short term N toxicity
Long term N toxicity
Angling/Stocking
Birds/flyway
Average of Human Mediated:
3. Average of risks
# Ranking: 6=uncertain 5=very high, 4=high, 3=medium, 2=low, 1= very low
*Certainty=(.75lab or .90 field)*(source: 0.9 peer reviewed, .8 thesis, .7 report, .6 personal communications)*(1-(tested temp-facility temp)*.1)*(.5 if source
population is different)*(.8calculated or .9 for given)*(.5 if not NZMS)
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4. Passive Spread Potential
Known
Population 6-uncertain
5-very
high 4-high 3-medium 2-low 1-very low
Facility
ranking
Distance not known <10 miles
<50
miles
within
state
neighboring
state
not in
country
Density not known >100,000 >10,000 >1,000 >100 >1
4. Total risk ranking
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Probability of Establishment
1.&2. Pathways
3. Colonization 4. Spread Risk of
Establishment
Calculated Risk of Establishment Risk Ranking
Uncertain
Very high
High
Medium
Low
Very Low
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Consequences of EstablishmentExample risks Ranking level
5. Estimate of economic
impactBased on Federal and State
regulations
6. Environmental effects
potential
Reduction or elimination of
endangered/threatened species
Loss of quality habitat
Increase disease in fish and
bird populations
Reduction in native
biodiversity from less or
elimination of quality
preferred habitat
7. Social and cultural
influences
Can have positive and
negative connotations
(+) increased amount of
decomposition
(-) loss of anglers in region
Total risk:6-uncertain 5-very high 4-high 3-medium 2-low 1-very low
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Consequences of Establishment
Calculated Consequences of Establishment Risk Ranking
Uncertain
Very high
High
Medium
Low
Very Low
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Risk potential (average of the two)Probability of Establishment Consequences of Establishment
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Status of FacilityNot Infested Infested
Risk potential (average of the two)Probability of Establishment Consequences of Establishment
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Choices/ConstraintsPrevention Status Quo Manage Eradicate
Status of FacilityNot Infested Infested
Risk potential (average of the two)Probability of Establishment Consequences of Establishment
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Choices/Constraints• Determine if facility is infested or not infested
– If not infested choices:• Status Quo• Prevention
– If infested choices:• Status Quo• Manage • Eradicate
– Once facility clean follow not infested choices
• Review of all regulatory constraints– Threatened/endangered– Permits: chemical, transport, etc.– NPDES
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RecommendationsAssess Critical Control Points Use tools to lower risk
Choices/ConstraintsPrevention Status Quo Manage Eradicate
Status of FacilityNot Infested Infested
Risk potential (average of the two)Probability of Establishment Consequences of Establishment
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Recommendations
• Assess Critical Control Points through HACCP process
• Use tools to lower risk - Prevention
– Different tools will be incorporated at the Critical Control Points to manage or eradicate
• Response Planning and Protocols
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Chemical Tools
• Can be used to kill NZMS in foot baths and gear disinfections- closed containers
• Limited research in open water for large scale disinfections
• High environmental contamination risks
• Bath application only, NO SPRAY APPLICATIONS
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Certainty Determined By
• Number of replicate trials and temperatures tested
• Replications by different investigators with similar results
• Evaluating presence of neonates
– Stressed adults will release viable neonates
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Chemical Certainty
Chemical Certainty
Virkon Aquatic Very High
Sparquat 256 Very High
Formula 409 All Purpose Cleaner Very High
Ammonia High
Copper sulfate High
Pine-Sol High
Formula 409 Degreaser and Disinfectant High
Copper sulfate Medium
Hydrogen Peroxide Medium
Pine-Sol Medium
Benzethonium chloride Medium
Hyamine Medium
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Physical Tools• Filtration
– Drum, hydrocyclone, mesh screens, sieves
• Freeze or Heat– Boiling water or fire
• Depuration Strategies• Mixed Cell Raceway• Barriers
– Copper, electrical, velocity, aeration
• Removal– Suction dredge, disturbance-cleaning
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Tool Certainty Determined
• For each source
– Percent effective
– Calculated/ given
– Neonates
– Lab/ field
– Type of data
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Tool Certainty
Tool Certainty levelHydrocyclone High
Freezers High
Depuration Strategies High
Sieves Medium
Screen Filter Medium
Boiling Water Medium
Fire Medium
Copper Barrier Medium
Drum Filter Low
Mixed Cell Raceway Low
Electrical Barrier Low
Velocity Barrier Low
Aeration Barrier Low
Suction Dredge Low
Disturbance Low
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RecommendationsAssess Critical Control Points Use tools to lower risk
Choices/ConstraintsPrevention Status Quo Manage Eradicate
Status of FacilityNot Infested Infested
Risk PotentialProbability of Establishment Consequences of Establishment
Adaptive Process
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• New tools for monitoring & disinfection
• New approaches for management
• Validate each tool within target facility
• Applicable to multiple species or facilities
• Be prepared for surprises
Utilization of New Information